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Greener energy has a positive impact on manufacturing

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Sameer Kumar Pujari, Senior General Manager, JK Cement, elaborates on the role played by technology, alternative raw materials, cost, infrastructure and local regulations in making cement manufacturing process more energy efficient.

Tell us about the role of energy in the manufacturing of cement? What is the volume of your organisation’s energy consumption?
The role of energy in the manufacturing of cement is significant as it is one of the most energy-intensive industries globally. The production of cement involves several energy-intensive processes, from the extraction and crushing of raw materials to production of clinker and finally converting it into cement.
The production of cement consumes large quantities of energy in the form of thermal and electrical. This requires approximately 3.2 GJ to 5.0 GJ of energy per tonne of clinker produced. As an energy intensive industry, thermal energy used in the cement industry accounts for about 20–25 per cent of the production cost. The typical electrical energy consumption of a modern cement plant is about 70 KWh to 80 KWh per tonne of cement. In the manufacturing process, thermal energy is used mainly during the burning process, while maximum share of electrical energy is used for cement grinding.
Our SEC is approximately 61.8KWH/T cement and specific thermal energy is 3.18 GJ/tonne of cement. We are proud to share that our IU at Muddapur Karnataka and GU at Jhajjar, Haryana, are national leaders in energy and have been awarded by renowned organisations like Confederation of Indian Industry (CII). The source of energy in cement manufacturing is fossil fuels (coal, oil and natural gas) and alternative fuels (biomass/waste material/municipal waste etc.).
Other than above, we also use renewable energy solar/wind, WHRS and grid power to produce cement.

What are the various modes of energy sources used by your organisation for its manufacturing needs?
We use fossil fuels as the energy source for manufacturing needs. This includes coal, oil, and natural gas, which are burned in kilns to generate the heat necessary for the production process. We are also utilising alternative fuels to reduce usage of fossil fuels and promote sustainable practices. These alternative fuels can include RDF, biomass, such as rice/mustard husk or agricultural waste as well as waste materials like shredded tires or sewage sludge. By using these alternative fuels, we are not only progressing towards carbon neutrality but also contributing to waste management efforts.
We are using solar, wind and WHRS, too. We are procuring renewable energy through open access. Our capacity in WHRS is 62 MW, solar is 20 MW and we are progressing towards the goal of green cement by 2030. Our Muddapur, Karnataka, plant has achieved 100 per cent renewable energy uses at zero grid consumption through open access.

Which of the said energy sources yields maximum productivity for the plant and which yields the least?
The productivity of different energy sources for cement plants can vary depending on various factors such as technology being used, availability, cost, infrastructure and local regulations. Here are some examples:

Fossil fuels (e.g., coal, oil, and natural gas): Traditionally been the primary energy source for cement production due to their high energy content. However, they contribute significantly to carbon emissions and are considered non-renewable resources.
Biomass: Biomass, such as agricultural residues or dedicated energy crops, can be used as an alternative fuel source in cement production. Its productivity can vary depending on the availability and sustainability of biomass feedstock.
Waste materials: Certain waste materials, such as shredded tires or municipal solid waste, can be used as alternative fuels in cement kilns. The productivity of waste materials as an energy source depends on their calorific value, availability, and proper waste management practices.
Renewable energy sources: Renewable energy sources like solar, wind or geothermal power can be utilised to generate electricity for cement plants. Their productivity depends on factors such as location, resource availability and the ability to integrate them into the plant’s
energy infrastructure.
It is important to note that each cement plant may have unique circumstances and considerations when choosing an energy source. The optimal solution often involves a combination of different energy sources and technologies to achieve maximum productivity while minimising environmental impact.

What are the alternative energy sources that are being adapted by the cement industry and your organisation?
Generally fossil fuels such as coal, petroleum coke and natural gas provide the thermal energy required for the cement industry. With increasing economic benefits in usage of alternative fuel (AF) over conventional fuels gives high thrust on usage of AF. Other factors, which give a push to usage of AF, are limited resources of fossil fuel and environmental concerns. AF covers all non-fossil fuels and waste from other industries including tire-derived fuels, biomass residues, sewage sludge and different commercial wastes. The kiln used in cement manufacturing is able to burn a wide range of materials due to the long exposure time at high temperatures (up to 1400oC), intrinsic ability of clinker to absorb and lock contaminants into the clinker and the alkalinity of the kiln environment. Materials like waste oils, plastics, waste tires and sewage sludge are being adopted as alternative fuels by the cement industries. Biomass waste and spent pot linings produced in aluminium smelters are also identified as potential alternative fuels for the cement industry.
Our organisation uses almost all kinds of plastic wastes, non-hazardous and hazardous waste, and biomass. We have a dedicated AFR feeding system in our plants. We initially focused on using plastic waste, shredded RDF. Slowly and gradually, we increased our capacity and started using hazardous materials also. For the processing of hazardous waste, we needed impregnation material like biomass such as rice husk, saw dust, wood chips, etc. So, we started utilising them in smaller proportions. And with the experience so far, now we are consuming around 20 per cent to 25 per cent of hazardous solid waste, 40 per cent to 50 per cent MSW/RDF waste, and up to 25 per cent non-hazardous solid wastes.

What is the impact of greener energy sources on the productivity and cost of cement manufacturing?
Greener energy has a positive impact on manufacturing, including commercial and technical aspects. Here are some potential impacts:
Productivity: Greener energy sources have a positive impact on the productivity of cement manufacturing. For example, using alternative fuels like biomass or waste materials can
provide a reliable and consistent source of heat for kilns, ensuring a stable production process. This can help reduce downtime and improve overall productivity.
Cost: The cost implications of using greener energy sources in cement manufacturing can also vary. In some cases, alternative energy sources may be more cost-effective compared to traditional fossil fuels as AF gives additional revenue to consumers of AF. Additionally, utilising waste materials as alternative fuels can reduce waste disposal costs for cement plants.
Energy efficiency: Greener energy sources often promote energy efficiency in cement manufacturing. For example, using renewable energy sources like solar or wind power can reduce reliance on fossil fuels and decrease energy consumption. This can result in cost savings and improved overall efficiency.
Environmental impact: One of the key benefits of greener energy sources in cement manufacturing is the reduction in environmental impact. By transitioning to alternative fuels or renewable energy sources, cement plants can significantly reduce greenhouse gas emissions and air pollution associated with traditional fossil fuel combustion. This can contribute to environmental sustainability goals and help meet regulatory requirements.
It is important to note that the specific impact on productivity and cost will depend on the individual circumstances of each cement organisation, including factors such as location, availability of resources, technological capabilities and government policies or incentives.

How does automation and technology help in optimising the use of energy in cement plants?
Automation and technology play a pivotal role in optimising the use of energy in cement plants. We are using VFD, Smart MCC, Sensors, Integrated Load Management System, Energy Monitoring System and Smart Lighting System for effectively optimising the use of energy in our organisation.
Here are some ways which helps to reduce the energy:
Energy monitoring and control: Automation systems can continuously monitor energy consumption in various parts of the cement plant, such as kilns, mills, and crushers. This real-time data allows operators to identify pilferage processes or equipment and optimise energy usage.
Process optimisation: Advanced control systems and predictive analytics can optimise the cement manufacturing process to minimise energy consumption. By analysing data from various sensors and instruments, these technologies can identify opportunities for energy savings and automatically adjust parameters to achieve optimal efficiency.
Energy management systems: Automation systems can integrate with energy management systems to provide a holistic view of energy usage across the entire plant. This allows operators to track energy performance and accordingly set targets, and implement energy-saving measures effectively.
Load management: Automation systems can optimise the scheduling and sequencing of equipment to ensure a balanced load distribution, reducing peak demand and improving overall energy efficiency. For example, by coordinating the operation of kilns, mills, and other machinery, the system can minimise energy wastage during periods of low demand.
Energy recovery: Automation technology can facilitate the implementation of energy recovery systems in cement plants. For instance, waste heat from kilns can be captured and used to generate electricity or provide heat for other processes, reducing the reliance on external energy sources.
Equipment optimisation: Automation systems can monitor the performance of individual equipment and identify inefficiencies or malfunctions that may contribute to excessive energy consumption. By providing real-time alerts and diagnostics, operators can take corrective actions promptly, ensuring optimal equipment performance and energy usage.
Overall, automation and technology enable cement plants to have better visibility, control and optimisation of energy usage. This leads to improved energy efficiency, cost savings and reduced environmental impact.

What are the major challenges your organisation faces in managing the energy needs?
We are facing challenges of imposition of power curtailment from grid mostly at our Rajasthan-based plants:
• Grid disturbances and power outages
• There is high volatile market and heavy fluctuations in fuel sourcing
• Energy cost volatility: Cement production is highly energy-intensive, and the cost of energy can fluctuate significantly. This makes it challenging to plan and budget for energy needs effectively an increase in the prices of fossil fuel
would adversely impact the industry, leading to an increase in production costs, however we focused on driving optimisation of fuel mix, energy efficiency and use of alternative fuel to mitigate this
• Ageing infrastructure: To upgrade or replace the ageing infrastructure/ systems can be expensive and may require significant downtime. However, we have completed the brownfield modernisation of our Nimbahera Line-3, with the kiln now capable of producing 6,500 TPD, against the earlier capacity of 5,000 TPD. The brownfield projects that have been undertaken over the past few years have been delivering greater efficiencies in the form of reduced power and fuel consumption and increased WHR.

Tell us about the compliance and standards followed by you to maintain energy use and efficiency in the organisation.
Some of the key regulations and standards include:
ISO 50001: This international standard provides a framework for organisations to establish, implement, maintain, and improve an energy management system. We are ISO 50001 certified company and regularly enhance our energy performance, identify energy-saving opportunities and comply with energy management requirements.
PAT Compliance: PAT is a mechanism for improvements in energy efficiency of energy intensive industries. Specific high energy intensive industries are identified as Designated Consumers (DC) within certain key sectors, who are required to appoint an energy manager, file energy consumption returns every year and conduct mandatory energy audits regularly. The key tasks in the PAT mechanism is to set the methodology for deciding the Specific Energy Consumption (SEC) norms for each designated consumers in the baseline year and in the target years, devise verification process for SEC, finding ways of issuing the Energy Savings Certificates, operationalisation of the trading process for ESCert in addition to the compliance and reconciliation process for ESCert.
To ensure compliance with these regulations and standards, JK Cement regularly monitors our energy consumption, implements energy management systems, conducts energy audits, invests in energy-efficient technologies, and reports the emissions and energy performance to relevant authorities. Additionally, we collaborate with industry associations, research institutions and government agencies to stay
updated on evolving regulations and best practices in energy management.

How often are audits done to ensure optimum use of energy? What is the suggested duration for the same?
• We conduct energy audits every year as a part of energy management practices. This allows us to assess the energy performance, identify
areas for improvement and implement energy-saving measures.
• We have formed internal management teams across our plants where we closely monitor
our energy consumption on a daily basis. We fix our best targets across the locations
and further compare and revise our targets to further optimisation.

What kind of innovations in the area of energy consumption do you wish to see in the cement industry?
Some potential innovations in the area of energy consumption that we may wish to see in the cement industry:
Alternative fuel sources: Increased utilisation of alternative fuels, such as biomass, waste materials, or renewable energy sources, can reduce reliance on fossil fuels and lower carbon emissions.
Energy-efficient technologies: The adoption of advanced technologies, such as more efficient kilns, improved heat recovery systems, and optimised grinding processes, can help reduce energy consumption in cement production.
Carbon capture and utilisation: Implementing carbon capture, storage, and utilisation (CCUS) technologies can help capture and store carbon dioxide emissions from cement plants or utilise them in other industrial processes.
Process optimisation through AI: Continuous process optimisation through AI data analytics, machine learning, and automation can identify areas of inefficiency and enable real-time adjustments to optimise energy consumption.
Circular economy practises: Adopting circular economy principles, such as recycling and reusing waste materials or by-products from cement production, can reduce resource consumption and minimise environmental impact.
Collaborative research and development: Encouraging collaboration between industry stakeholders, researchers and governments can drive innovation in energy-efficient cement production technologies and practices.
• We want to innovate to produce entirely green cement with sustainability and to achieve our net zero target by 2030.
• Cement manufacturing with an alternative of fly ash and lesser water curing requirements also plants with less heat consumption during clinker production such as in LC3 cement.

-Kanika Mathur

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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Concrete

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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Concrete

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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