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Salient points of Occupational Safety, Health and Working Conditions Code, 2019

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Ensuring occupational safety, no harm to existing health and proper working condition for all the workforce in every enterprise is a necessary and essential requirement for running any business, In India we have four main legislations that cover Occupational Safety and Health at workplace. (i) The Factories Act, 1948 , covering factories wherein the enforcement of safety at workplace is by the Chief Inspector of Factories in the respective states, (ii) The Mines Act, 1952 and Mines Rules, 1955 for mining industry where the enforcement is by Directorate General of Mines Safety (DGMS) under Ministry of Labour & Employment , Government of India, (iii) The Dock Workers (Safety, Health and Welfare) Act, 1986 followed by notification of the Dock Workers (Safety, Health and Welfare) Regulations, 1990 dealing with the major ports of India and the enforcement is by Director General, Directorate General of Factory Advice Service & Labour Institutes (DGFASLI), under Ministry of Labour & Employment, Government of India, and (iv) The Building & Other Construction Workers (Regulations of Employment and Conditions of Service) Act, 1996, covering construction workers at construction sites wherein the enforcement is by the State Government.

The Second National Commission on Labour submitted its Report on ??ccupational Safety, Health and Working Conditions of the Workers??in June, 2002 and made certain recommendations including the need to consolidate various laws. In pursuance of the recommendations of the said Commission, the National Democratic Alliance Government has introduced Bill Number 186 of 2019 on 23 July 2019 called ??he Occupational Safety, Health and Working Conditions Code, 2019??in the Lok Sabha, which has 134 clauses and three schedules. While the schedule one and three are identical to the schedules in The Factories Act ,1948, but the schedule two covers many items relevant to occupational safety, health and working conditions. The Code will subsume 13 labour laws and would apply to all establishments employing 10 or more workers. These include (a)The Factories Act, 1948; (b) The Mines Act, 1952; (c) The Dock Workers (Safety, Health and Welfare) Act, 1986; (d) The Building and Other Construction Workers (Regulation of Employment and Conditions of Service) Act, 1996; (e) The Plantations Labour Act, 1951; (f) The Contract Labour (Regulation and Abolition) Act, 1970; (g) The Inter-State Migrant Workmen (Regulation of Employment and Conditions of Service) Act, 1979; (h) The Working Journalist and other News Paper Employees (Conditions of Service and Miscellaneous Provision) Act, 1955; (i) The Working Journalist (Fixation of rates of wages) Act, 1958; (j) The Motor Transport Workers Act, 1961; (k) The Sales Promotion Employees (Conditions of Service) Act, 1976; (l) The Beedi and Cigar Workers Act, 1966; (m) The Cine Workers and Cinema Theatre Workers Act, 1981 (details refer section 134). Presently each of these 13 labour laws have Rules and we still have to await the Rules that the Central Government frames for this code, which can be the same or modified by the State Governments.

This code is one of the four labour codes and is currently referred to the Parliamentary Standing Committee for consideration, and hence will take some time, before it gets passed by the Lok Sabha and becomes an Act. The rules with reference to the Code have still to be framed and made public.

Given below are summary analysis of certain relevant sections in the code:

Section 2 of every labour legislation deals with definitions. Since, this code is to replace 13 labour legislations which deal with various aspects apart from the area of Occupational Safety, Health and Working Conditions the definition of the words in section 2 needs to be understood and analysed, to realise the modification where they are taking place through the code. In most cases, the word as defined in the code is a continuation of the definition in one of the 13 acts, but in certain cases the same has been modified and hence has implications of applicability.

Section 2 (g): In ??uilding or other construction work??the definition specifies that it does not include any building or other construction work of any factory or mine or any building or other construction work employing less than ten workers.

Section 2 (u): The term ??stablishment??has been defined as a place where any industry, trade, business, manufacture or occupation is carried on in which ten or more workers are employed; or a factory, motor transport undertaking, newspaper establishment, audio-video production, building and other construction work or plantation, in which ten or more workers are employed; or a mine or dock work. The word ??stablishment??is used in many of the sections

Section 2(zb)(b): The term ??ndustry??does not include domestic service.

Section 2(zo): The term Occupier has been modified compared to The Factories Act, 1948 and an independent director cannot be an occupier.

Section 2(zz): The term ??ales promotion employees ??efinition does not include apprentices as specified in The Sales Promotion Employees (Conditions of Service) Act, 1976;

Section 8 specifies duties of manufacturers, designer, importers or suppliers and holds them responsible for the safety of the equipment and material designed, imported, supplied, erected, installed as to be safe and without risk to the health of the workers when properly used. There are details specified which were not covered in the existing legislations.

Section 9 in detail specifies the duties of architects, project engineers and designers and holds them responsible for ensuring that they have considered all aspects of safety and health for the workers that are carrying out the construction, but to also take into account the safety aspects associated with the maintenance and upkeep of the structures and buildings where maintenance and upkeep may involve special hazards.

Section 12: (1) and 12(2) deal with notice of certain diseases and these sections are identical to section 89 and 90 of The Factories Act, 1948 except the word factory has been replaced by the word establishment. Also, the Schedule Three specifying list of notifiable diseases is identical to the schedule three in The Factories Act, 1948.

Sectior 16 and 17 deal with constituting a National Occupational Safety and Health Advisory Board and State Occupational Safety and Health Advisory Board which is something new compared to the present legislation. Section 18 deals with occupational safety and health standards and the second schedule is a very exhaustive list covering list of matters to be covered in factories, mines, ports, construction, offices, plantation and others. The second schedule under section 41-F of The Factories Act, 1948 which dealt with permissible limits of 116 chemical substances is not to be found in the second schedule of the code and since the schedule mentions that ??he Central Government shall declare, by notification, standards on occupational safety and health for work places relating to factories, mines, dock work, building and other construction work and other establishments ??robably these will be specified later .

Section 21 deals with an effective programme of collection, compilation and analysis of occupational safety and health statistics.

Section 22 deals with Safety Committee and safety officers in establishments.

Section 24 deals with welfare facilities in the establishment and in subsection (2) specifies bathing places and locker rooms for male, female and transgender employees separately. This is a recognition of accepting the employment of transgender employees at the work place.

Section 25 deals with weekly and daily working hours, leave, etc. and since the Code also covers sales promotion employees. It is silent on the working hours of sales promotion employees but specifically in sub – section (3) in detail specifies the leave benefits. It has to be seen how this will get interpreted, as sales promotion employees have to work when they can meet the doctors and the eight hours working per day cannot be from 9 am to 5 pm like the general shift of establishments.

Section 37 provides for a third-party audit and certification for start-up establishments and class of other establishments to get the same done and submit their reports to the concerned employer and Inspector-cum-Facilitator separately for the purpose of ensuring compliance of the provisions of this Code.

Section 43 provides for women to work in with her consent, to be employed in an establishment before 6 a.m. and beyond 7 pm.

Section 45 to 62 deal with contract Labour and Inter State Migrant worker, as both these Acts have been merged with this code.

Section 50 (1) states that when a contractor receives work order from an establishment, he has to intimate the same to the appropriate Government.

Section 60(1) the contractor to every inter-State migrant worker at the time of recruitment, has to pay a displacement allowance equal to fifty per cent of the monthly wages payable to him which was already there in the existing act.

Section 73 states that a person who is deaf or has a defective vision or has a tendency to giddiness be not employed in building or other construction work which is likely to involve a risk of any accident either to the building worker himself or to any other person. This is keeping safety in mind.

Section 75 deals with premises or buildings leased to different occupiers for use as separate factories, the owner of the premises and occupiers of the factories utilising such common facilities include safety and fire prevention and protection, shall jointly be responsible for providing maintenance of common facilities and services as may be prescribed.

Section 83 deals with maximum limit of exposure of chemical and toxic substances in manufacturing process in any factory. Earlier these limits were specified in Schedule Two of The Factories 1947. Act, Under the code these are not specified and it is mentioned that the limits of exposure of chemical and toxic substances in manufacturing process in any factory will be decided by the State Government.

Section 87 deals with general penalty which shall not be less than Rs 2 lakh to the employer of any establishment for the contravention of the code.

Section 96 (1) deals with a dangerous occurrence resulting in (a) death, then the person responsible shall be punishable with an imprisonment for a term which may extend to two years or with a fine which shall not be less than Rs five lakh or with both.

Section 107 (1) deals with compounding of offence and its procedure.

However, this compounding is only applicable for offence in which the punishment does not involve imprisonment.

Conclusion

The Code is an effort by the Ministry of Labour & Employment, Government of India at combining 13 labour laws which not only dealt with safety, health and working conditions plus other areas relevant to the workers employed in factories, mines, docks, building and construction, plantation, motor transport, beedi and cigar, cine and cinema theatre, journalism, field force, plus the contract workers and interstate migrant workers.

Presently a large number of enterprises are engaging contract labour through contractors/ service providers under the existing Contract Labour (Regulation and Abolition) Act, 1970. It is to be seen how the proposed code will impact the employers, contractors and contract workers once the Rules to the Occupational Safety, Health and Working Conditions Code, 2019 are released.

There are techniques such as ??ontrolled Implosion??which can be used for swift demolition of structures and there was need that these from the point of occupational safety and health should have been included in the Code , Also new forms of employment based on App Platforms that have entered the business area have not been dealt with, as we need to also look at their occupational safety, health and working conditions

Since the code subsumes 13 labour laws the terminology of enterprise is used in most sections. Since this code is going to replace legislations of 1948 and later, it is too early to predict how this legislation will help the workers, trade unions and employers associated with enterprises in India in ensuring occupational safety and improved health. The acid test on the clarity of a legislation comes with judicial interpretations.

ABOUT THE AUTHOR:

Dr Rajen Mehrotra is past President of Industrial Relations Institute of India (IRII), Former Senior Employers??Specialist for South Asian Region with Internation.al Labour Organization (ILO) and Former Corporate Head of HR with ACC, and Former Corporate Head of Manufacturing and HR with Novartis India Ltd. Email: rajenmehrotra@gmail.com

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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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