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Grinding aids help in reducing the agglomeration of particles

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Lokesh Chandra Lohar, General Manager – Technical and Executive Cell, Wonder Cement, shares insights on overcoming challenges, leveraging innovations and the crucial role of R&D in maintaining high standards in cement production.

Can you provide an overview of the grinding process in your cement manufacturing plant and its significance in the overall production process?
Cement grinding unit is used to grind clinker and gypsum into a fine powder, known as cement. The process of grinding involves grinding of the clinker to a fine powder, which is then mixed with gypsum, fly ash and other additives to produce cement.
At Wonder Cement, our grinding processes are pivotal in ensuring high-quality cement production by utilising state of art technologies ex. Vertical Roller Mill (VRM), roller press with ball mill in combi circuit and finish mode grinding and high-efficiency classifier, have achieved optimal particle size distribution and energy efficiency.
Our commitment to sustainability is evident with usage of energy-efficient equipment, eco-friendly grinding aids and renewable energy sources. Continuous research and development efforts ensure we stay at the forefront of innovations, optimising our grinding operations and minimising impact on the environment.

The main processes involved in a cement grinding unit are:

  • Clinker grinding: This is the main process in a cement grinding unit, where the clinker is ground into a fine powder using a ball mill or combi mills (RP+ Ball Mill) or vertical roller mill circuit. The grinding process is controlled to achieve the desired fineness of the cement.
  • Gypsum and other additives: Gypsum is added to the clinker during the grinding process to regulate the setting time of the cement. Other additives such as fly ash, BF slag and pozzolana may also be added to improve the performance of the cement.
  • Packaging: Once the grinding process is complete, the cement is stored in silos before being packed in bags or loaded into bulk trucks for transportation.
  • Quality control: Quality control measures are in place throughout the grinding process to ensure that the final product meets the required specifications, including strength, setting time, and consistency.What are the main challenges you face in the grinding process, and how do you address these challenges to maintain efficiency and product quality?
    The main challenges in the grinding process include high energy consumption, frequent wear and maintenance, variability in clinker properties, environment impact and ensuring consistent product quality. To address these challenges, we have implemented several strategies:
  • High energy consumption: Clinker grinding is energy-intensive, and high energy costs can significantly impact the overall production costs of cement.
    This is one of the primary challenges in the grinding process.
  • Use of high-efficiency equipment: We have state-of-the-art energy-efficient grinding equipment, such as vertical roller mills (VRM), Combi Circuit (roller press with ball mill), which consume significantly less energy consumption.
  • Process optimisation: Real time monitoring and optimisation of the grinding process to minimise energy consumption.
  • Frequent wear and maintenance: The grinding equipment, such as mills and crushers, is subjected to wear over time. Frequent maintenance and downtime can affect production efficiency.
  • Regular maintenance: Implement a proactive maintenance schedule to address wear and tear promptly, ensuring the equipment remains in optimal condition.
  • Proper lubrication: Adequate lubrication of moving parts can extend the lifespan of grinding equipment.
    Use of wear-resistant materials for components, which are prone to wear and abrasion.
  • Variability in clinker properties: Clinker properties can vary from one batch to another, leading to inconsistencies in the grinding process and the quality of the final cement product.
  • Clinker sources: At Wonder we have one clinker source, which is our mother plant at Nimbahera, Rajasthan and we distribute clinker to various split GU’s from Nimbahera. This helps us to maintain uniform clinker quality across each location.
  • Quality control: Rigorous quality control measures help us identify and address variations in clinker properties. Adjust grinding parameters as needed to compensate for these variations. (ex. use of cross belt analyser and on-line particle size distribution)
  • Environmental impact: Energy-intensive grinding processes can have environmental repercussions due to high dust emissions and energy consumption.
    Use of high efficiency dust collection and suppression system to keep emissions below statutory norms
  • Sustainable grinding aids: Consider using eco-friendly grinding aids that enhance grinding efficiency without compromising cement quality and environmental standards.
  • Alternative fuels: Use alternative and more sustainable fuels in the cement kiln and hot gas generated to reduce carbon emissions.
  • Use of clean energy in logistics:
    To reduce carbon emissions, sustainable alternatives are also sought for inland transport. We have involved neutral internal transports (electric powered trucks).
  • Automation and digitalisation of production:
  • Wonder Cement has already initiated the process to implement Smart Cement Industry 4.0.
  • With Industry 4.0, the automation and digitalisation of operations, including the use of sensors, remote diagnosis, analysis of big data (including the artificial intelligence analysis of unstructured data such as images and video), equipment, virtual facilities, and intelligent control systems will be done automatically (based first on ‘knowledge capture’ and then on machine learning). For Process optimisation we are using the FLS Process expert system (PXP) system. This allows for system optimisation and increased efficiency gains in production.

How do grinding aids contribute to the efficiency of the grinding process in your plant? What types of grinding aids do you use?
Grinding aids help in reducing the agglomeration of particles, thus improving the overall grinding efficiency and ensuring a smoother and more efficient grinding process without having adverse effect on any of the properties of the resulting cement. In cement manufacturing, various types of grinding aids are used to improve the efficiency of the grinding process. These include:

Glycol-based grinding aids

  • Composition: Ethylene glycol and diethylene glycol.
  • Usage: Commonly used in to improve the grinding efficiency and reduce energy consumption.

Amine-based grinding aids

  • Composition: Triethanolamine (TEA) and Triisopropanolamine (TIPA).
  • Usage: Effective in improving the grindability of clinker and other raw materials, enhancing cement strength and performance.

Polyol-based grinding aids
Composition: Polyethylene glycol and other polyol compounds.
Usage: Used to improve the flowability of the material and reduce the tendency of particles
to agglomerate.

Acid-based grinding aids
Composition: Various organic acids.
Usage: Used to modify the surface properties of the particles, improving the grinding efficiency and final product quality.

Specialty grinding aids

  • Composition: Proprietary blends of various chemicals tailored for specific materials and grinding conditions.
  • Usage: Customised to address challenges in the grinding process, such as the use of alternative raw materials or specific performance requirements.

Can you discuss any recent innovations or improvements in grinding technology that have been implemented in your plant?
Recent innovations and improvements in grinding technology:

  • Selection of state-of-the-art vertical roller mills along with high efficiency classifier (VRMs): VRMs are more energy-efficient and have lower power consumption, leading to significant energy savings. They also provide a more consistent product quality and require less maintenance. For raw meal grinding, we have both VRM and roller press.
  • Wear-resistant materials and components: Upgrading grinding media, liners and other components with wear-resistant materials. These materials extend the lifespan of the equipment, reduce downtime, and lower maintenance costs. Examples include ceramic liners and high chrome grinding media.
  • Intelligent monitoring and predictive maintenance: Utilising IoT sensors and predictive analytics to monitor equipment health. Predictive maintenance helps identify potential issues before they lead to equipment failure, reducing unplanned downtime and maintenance costs. It ensures optimal performance and prolongs equipment life.
  • Optimisation software and simulation tools: Using simulation software to model and optimise the grinding process. These tools help in understanding the process dynamics, identifying bottlenecks, and testing different scenarios for process improvement. This leads to better process control and efficiency.

How do you ensure that your grinding equipment is energy-efficient and environmentally sustainable?

  • Energy-efficient grinding technologies such as VRMs: VRMs are more energy-efficient than traditional ball mills due to their ability to grind materials using less energy.
  • Benefits: Up to 30 per cent to 40 per cent reduction in energy consumption.
    Use of renewable energy sources (solar power integration): Utilising solar power for grinding operations
  • Implementation: Signing of long-term open access power purchase agreements (PPA) with renewable energy developers
  • Benefits: Reduces reliance on fossil fuels, decreases greenhouse gas emissions.

Environmental sustainability practices

a. Dust collection and emission control
Description: Using bag filters, and covered material handling system
Implementation: Installing and maintaining high-efficiency dust control equipment.
Benefits: Reduces particulate emissions, improves air quality, complies with environmental regulations.
b. Water conservation
Description: Recycle and reuse water in the grinding process.
Implementation: Installing sewage treatment plant (STP)
Benefits: Reduces water consumption, minimises environmental impact.
c. Use of alternative raw materials
Description: Incorporating industrial by-products like fly ash, BF slag and chemical gypsum in the grinding process.
Implementation: Sourcing and blending alternative materials.
Benefits: Reduces the need for natural resources, lowers carbon footprint, enhances sustainability.
By implementing these practices, the plant ensures that its grinding operations are both energy-efficient and environmentally sustainable, aligning with industry best practices and regulatory requirements.

What role does research and development play in optimising your grinding processes and the selection of grinding aids?
Following is the role of research and development in optimising grinding processes and selecting
grinding aids:

  • Testing and usage of new low-cost cementitious material: Dedicated R&D teams work on developing and new low-cost cementitious material to reduce clinker factor in cement and
    improve efficiency.
  • Process simulation and modelling: Uses simulation and modelling tools to understand the dynamics of the grinding process and identify areas for improvement.
  • Formulation of new grinding aids with reverse engineering: Formulate new grinding aids to enhance the efficiency of the grinding process.
  • Testing and evaluation: Conducting laboratory and plant-scale tests to evaluate the effectiveness of different grinding aids.
  • Collaboration with industry partners: Collaborating with suppliers, universities and research institutions to stay at the forefront of grinding technology advancements.

Research and development play a crucial role in optimising grinding processes and selecting the appropriate grinding aids. By focusing on innovation, process optimisation, sustainability and continuous improvement, R&D ensures that the plant remains competitive, efficient, and environmentally responsible. This commitment to research and development enables the plant to achieve higher productivity, lower costs and produce superior quality cement.

What trends or advancements in grinding processes and grinding aids do you foresee impacting the cement manufacturing industry in the near future?
The trends and advancements in grinding processes and grinding aids that we see coming up in the near future are:

1. Digitalisation and Industry 4.0

  • Advanced process control (APC) and automation
  • Internet of things (IoT) and predictive maintenance
  • Artificial intelligence (AI) and machine learning (ML)

2. Energy efficiency and sustainability

  • Energy-efficient grinding technologies
  • Use of renewable energy

3. Innovations in grinding aids

  • Eco-friendly grinding aids
  • Tailored grinding aids
  • Multifunctional grinding aids

4. Advanced materials and components

  • Wear-resistant materials for liners
  • High-density grinding media

5. Process optimisation and integration

  • Holistic process optimisation

6. Sustainability and circular economy

  • Circular economy practices
  • Carbon capture and utilisation (CCU)

– 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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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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