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In Pursuit of Greener India

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For many cement companies in India, AFR represents an important business opportunity because it reduces fuel costs and CO2 emissions. By dealing safely with wastes that are often difficult to dispose of in any other way, cement manufacturers are able to provide an important service to society.

Cement production is characterised by an extremely high-temperature combustion process (up to 20,000?C flame temperature), necessary for heating and fusing the raw materials. The traditional fossil fuels most commonly used in this combustion process are coal, heavy fuel oil or gas. Substitution of these fossil fuels by alternative, waste derived fuels is a common practice in the cement industry, in many parts of the world. The nature of the production process makes it eminently suitable for this purpose – by ensuring full energy recovery from various wastes under appropriate conditions. Any solid residue from the waste then becomes a raw material for the process and is incorporated into the final cement clinker. Sometimes, waste can also be used to substitute raw materials in the process, thereby also conserving the natural resources generally used in the manufacture of cement.Why is this issue important?

Waste is an important issue for society – as an example, Europe alone produces more than 350 million waste tyres per annum. Recycling and disposal options for many waste materials and industrial by-products are often limited – used tyres is but one example. Where recycling is not possible, incineration or landfill is the most common disposal practice available for many wastes. However, by using waste as an alternative fuel or raw material in the cement-making process, there are benefits for society as well as to the cement maker. For many cement companies in India, it represents an important business opportunity, because it reduces fuel costs and CO2 emissions. By dealing safely with wastes that are often difficult to dispose of in any other way, cement manufacturers are able to provide an important service to society.

India can achieve 25 per cent thermal substitution rate (TSR) by 2025. In comparison to global standards, the country is far behind, as in many countries the substitution is 60-100 per cent. The main differentiator is the waste characteristics and the lack of support by the required agencies for generating a good segregated quality waste. This long term plan of achieving 25 per cent substitution rate, is as it is very challenging.

Challenges
Why achieving 25 per cent substation rate is a challenge, is very well explained by Milind Murumkar, Advisor – AFR, Vicat India Group. The main challenges faced by any cement manufacturer in use of Alternative Fuels & Raw Materials (AFR), which can be classified into four.

Managements ‘will’ to use and improve the AFR utilisation in its plants. Which means, creating a suitable environment and commitment in their people to achieve the targeted short and long term plans. Initially no one is willing to bring and use waste – which may have strong or unpleasant odour, may be difficult to handle, store and use – from other industries in their plant. Management thus needs to build and develop the infrastructure in a manner that it can use all types of industrial wastes be it solids, semi-solids or liquid.

Secondly, skill development and infrastructure is important, as AFR utilisation requires special skills in cement plants. In this case, engineers need to be properly trained to understand the waste characteristics, raw material and fuel characteristics; and the point of dosage in the kiln. This is mainly due to the fact that while using higher quantities of wastes in cement plants, process stabilities are maintained, which may otherwise affect the quality of product and production levels. A cement plant has to know its raw material composition and fuel composition to decide on the types of waste that can be used in their system and accordingly decide on the feeding points of different types of waste that need to be co-processed.

Murmukar further enlightens the regulatory requirements. There are specific rules and guidelines for hazardous waste during transportation, storage and usage, that the cement plants have to comply with, while using hazardous materials. The equipment and storage area etc., needs to be selected based on the availability of waste and the plants for next 10-15 years. Here Murumkar’s advice is to have proper market data mapping and long term agreements with the waste generators to build trust and confidence in them.

Lastly, understanding waste and waste generators, is the most challenging factor. It is necessary to understand the pain points of the waste generating industry and work on providing a total solution for managing their waste in an environmental friendly manner. Business success depends on having a good ‘win-win’ model between the cement plant and the waste generating industry. Waste generators need total solution for the different wastes generated. The success in utilisation of different types of waste in cement plant lies in having co-processing ability for providing total solution to the generating industry.

AFR for Greener India
As rightly simplify by UltraTech officials, the advantages of co-processing of alternate fuel in cement plant ranks higher in the waste processing hierarchy. This is because, high flame temperature (2,000?C) – ensures complete destruction of harmful pollutants. Residence time of combustion gases above 1,000?C in excess of three-four seconds – ensures complete destruction of pollutants. Plus, a complete destruction of organic compounds. Importantly, co-processing of AFR in cement ensures total neutralisation of acid gases, sulphur oxides and hydrogen chloride, by the active lime in the kiln load, in large excess to the stoichiometry. And, for the betterment of environment, there will be no production of by-products such as ash or liquid residue from gas cleaning.

Benefits of AFR is it produces overall environmental benefits by reducing releases to air, water and land. It also, maximises the recovery of energy while ensuring their safe disposal. Since, most of the cement plant use coal as a fuel, AFR definitely stands a chance to substitute coal, with savings made through resource conservation and associated CO2 emissions.

Meanwhile, one must understand that not every waste is suitable. In addition, according to Holcim, manufacturers must ensure that they do not impact product quality nor increase their atmospheric emissions by using a particular waste. At the same time, a key objective of AFR use is to achieve reductions in CO2 emissions. Meanwhile, stakeholder debate continues over the use of AFR in cement kilns. Some stakeholders are concerned about potential health or environmental impacts from the handling and combustion of alternative fuels. Others are concerned that product quality could be compromised. It has also been claimed that the use of waste and by-products as fuels actually perpetuates the production of these wastes, by offering a legal, cost-efficient solution to disposal.

However, other stakeholders are pleased by the ‘win-win’ possibilities of cutting GHG emissions and disposing of wastes by using AFR. It is therefore a challenge for cement manufacturers to manage stakeholder expectations and provide assurances to demonstrate their responsible use of these waste materials.

Cost Matter
Use of alternate fuels for TSR is a financial viable intervention with very good internal rate of return (IRR). It also depends on the type of waste proposed for usage and technical intervention. Many Indian cement plants have successfully implemented these options and substituted fossil fuel significantly. The payback period generally varies between two-four years.

Meanwhile, AFR is certainly beneficial in terms of earnings for the company (Refer Earning Benefits on page no 44). If managed properly, to have a blend of commodities and industrial waste in terms of TSR and thermi cost reduction, the benefits will be substantial. Unless AFR co-processing has a good economic viability, its long-term sustenance cannot be ascertained. The entire economic model needs to be such that the Rs/thermi is lower than that of fossil fuels.

Consistent Quality
Consistent supply and uniform quality are main constraints in utilising AFRs – for example, tyre carbon black. The cost of the carbon black depends upon the cost of waste tyres in the domestic market and import conditions. Due to high demand for waste tyres, the cost of carbon black is increasing and hence its adulteration too. There should be long term agreement with the manufacturers directly with clear quality parameters, thereby the traders can be avoided and can sustain the supply as well as quality. However, the essence of the agreement shall be the price factor with regards to the coal price. Regulatory authorities need to standardise all waste to streamline market operations.

Also, there is no existing standard for NOx from kiln Only SPM standard is 50 mg/Nm3 for new plants and 100 mg/Nm3 for old plants. NO2 standard from 1-1-2016 and SPM standard from 1-6-2016 for cement kiln will be 800 mg/Nm3 and 30 mg/Nm3, respectively. Now, most of the cement manufacturers have deployed online monitoring system and commissioned in plants stacks for monitoring SPM, SO2 and NOx. The online monitoring system has already started and likely to help manufacturers in controlling emissions while firing different type of AFRs.

Present Policy Framework
The Indian Waste Management policy frame-work, notified in 2016 is well designed for sustain-able waste management. It gives due recognition to co-processing. Its salient features are following.

  • These are based on the principle of Sustainability rather than disposal
  • Waste generator is required to manage his waste respecting the Waste Management Hierarchy and SPCBs are required to authorise the same. (Rule 4, HWM)
  • A facility is required to obtain authorisation from SPCB for receiving, storing, handling, transporting and pre-processing of wastes based on the availability of compliant infra-structure to handle them safely. (Rule 6, HWM)
  • Co-processing in cement plant is to be implemented based on the compliance to prescribed emission standards. Co-processing trial of any waste is not required anymore to receive authorisation for its co-processing. (Rule 9, HWM)
  • Interstate movement of wastes for recycling or co-processing is to be implemented by intimation to the respective SPCBs. (Rule 18, HWM)
  • Pre-processing centers to be developed rather than landfill sites
  • Convert SCF to RDF (Rule 15 (v), SWM)
  • For wastes recycling / utilisation (Rule 5.1 HWM)
  • Segregated Combustible Fraction (SCF) having calorific value >1500 Cal / gm to be sent to cement plant for co-processing (Rule 21.2, SWM)

The above provisions in the rules favor co-processing substantially. However, following is further required to be published by CPCB as mandated in the rules or for smooth implementation of these provisions in the rules
1.Guidelines on pre-processing and co-processing of wastes
2.Guidelines on co-processing of plastic wastes
3.Protocol for emissions monitoring from cement plants
The other important requirement that is desired to facilitate ease in achieving successful and responsible co-processing are following.
A)SPCBs must permit the waste generator to send his waste to any of the pre-processing or co-processing facility that is approved by SPCB of the respective State.
B)Transportation of the Hazardous wastes is per-mitted through a transporter that is approved by any of the SPCBs.

Social and Environmental Security
Different kinds of wastes that get generated during agricultural, industrial or municipal acti-vities pose severe environmental concerns to the society and can cause substantial damage to the environment in case they are not managed properly. All these wastes that may be hazardous or non-hazardous, can be co-processed in an envi-ronmentally sound manner in the cement kilns.

As per the new Waste Management Rules 2016, Government of India has abolished the earlier practice of granting waste by waste permit system. This system, says Ulhas Parlikar, Deputy Head, Geocycle India, ACC Ltd, "was in practice prior to the notification of these rules in which, the permit for undertaking co-processing of a waste used to be granted based on the review of the results of the co-processing trial of that particular waste."

"This action MoEFCC has implemented because the cement kiln co-processing has been demonstrated as an environmentally sound and ecologically sustainable solution for waste management," he added. To achieve this, according to Parlikar, environmentally compliant management of the wastes, proper control on inputs, process, output and emissions is required by way of implementing necessary facilities and process control measures.

The new Waste Management Rules 2016 have mandated that the permission for co-processing of all kinds of wastes can be granted by State Pollution Control Boards (SPCBs) based on the availability of the prescribed infrastructure in the plant to handle wastes in an environmentally sound & occupationally safe manner and while undertaking co-processing, compliance to the emission standards notified by MoEFCC for cement kilns undertaking co-processing. The Central Pollution Control Board (CPCB) has already prepared a circulated a draft of the pre- and co-processing guideline illustrating specific requirements to the stakeholders and is in the process of publishing the same after accommodating stakeholder comments.

Target: 25% TSR
Currently, the Indian cement industry’s average TSR is around four per cent, whereas the TSR in few countries are as high as 60 per cent (Austria, Germany). Now, with above stated challenges, it is a matter of interest to see how India will reach the set target of 25 per cent or more of TSR by 2025. A few is outlined by V Kannan, Counsellor, CII – Godrej Green Business Centre. The Government has already included necessary policy changes for adopting co-processing in the country. Further, capacity building on new rules and proper implementation of the rules will substantially increase co-processing levels in the country.

Under the Swachh Bharat Mission (SBM) and smart cities programme, management of municipal solid waste management (MSW) through sustainable practices is very vital. The new SWM rules also advocate source segregation of waste to channelise the waste-to-wealth by recovery, reuse and recycle. In addition, all industrial units using fuel and located within 100 km from a solid waste-based refuse derived fuel (RDF) plant shall make arrangements within six months from the date of notification of these rules to replace at least five per cent of their fuel requirement by RDF so produced. That apart, non-recyclable waste having calorific value of 1,500 K/cal/kg or more shall not be disposed of on landfills and shall only be utilised for generating energy either or through refuse derived fuel or by giving away as feed stock for preparing refuse derived fuel. And lastly, high calorific wastes shall be used for co-processing in cement or thermal power plants. Cement plants also working on various initiatives like pre-processing platforms, utilisation of hazardous waste, tie ups with urban local bodies to utilise MSW as a fuel increases TSR levels.

For experts to achieve the target there is an urgent need to implement necessary policy level reforms that are emission monitoring and infrastructure based. Further, there is a need for the cement industry to implement necessary facilities for waste handling, storing, pre-processing and feeding in the kiln. There is also investment required for creating facilities for monitoring and control of emissions. Further, the legislative process needs to bring the material in the market. For example, although, large quantities of tyres are replaced every year in the country, the same is not visible in the waste market. This is because there is no defined regulatory system in place to collect and divert them in the waste market. Once they become visible in the waste market, they will be available to the cement industry for disposal through co-processing.

Fact sheet

  • AFR substitution increased from less than 1% to more than 4% in 2016.
  • Recognition for co-processing in the policy framework.
  • >45 cement plants started co-processing in their production units.
  • Few state pollution control boards like Gujarat and Tamil Nadu, developed specific action plan & implementation schedule to promote co-processing.
  • >12 cement plants set up pre-processing facilities to convert non-homogeneous waste in to AFRs.
  • LCA (Life Cycle approach) is considered as a part of manufacturing process and extended producer responsibility.

Vicat’s proven track record
Vicat operates two plants in India as Kalburgi cement plant and Bharti cement plants, with an annual capacity of around 8 mtpa, to produce quality cement since 2009. Since the inception the focus was on utilisation of AFR material in both the plants and presently, Vicat could achieve TSR of around 20 per cent.

The journey started with substitution rate of around 5 per cent in 2012 and in last five years it has reached to a level of 20 per cent. The initial start-up was on utilisation of easy to use AF materials like biomass, segregated non-recyclable plastic waste etc. Presently, the company can co-process different types of waste like industrial wastes (hazardous and non hazardous), tyre derived waste, plastics derived waste, derived waste from MSW segregation process, animal waste, waste from windmill sources etc. The company also offers cradle to grave solution for different sectors like pharmaceutical industry, FMCG, tyre sector and municipal corporations for segregated MSW, food and beverage industries etc.

Understanding the main factors that led to this improvement in usage of AFR in Vicat will help the Indian cement industry have an introspection of their processes and preparedness for improving AFR utilisation in their plants.

Earning Benefits:
INCOME ITEMSEXPENDITURE ITEMS
Waste Generator
1.Sale price of Waste
2.Savings in cost of waste management due to co-processing
3.Reduction in the liability costs1.Tipping Fee for waste management
2.Marketing expenses
3.Pre-processing cost to convert waste into AFR

Cement Plant
1.Tipping Fees from waste generator
2.Substitution benefit derived due to use of AFRs1.Waste identification
2.Laboratory assessment
3.Handling and storage
4.Pre-processing cost to convert waste to AFR
5.Production impact
6.Fuel usage impact
7.Interest and Depreciation costs etc.

ACC: Leader in waste Management
The use of AFR essentially serves to move away from dependence on fossil-based fuels and other mineral resources.
In 2016, the company succeeded in co-processing 379,520 tonnes of AFR, achieving a TSR of 3.22 per cent. Following the commissioning and stabilisation of two pre-processing platforms and a third under execution, ACC expects the TSR percentage to increase in the long run, enabling company to cut its footprint even further.

ACC has taken the lead in providing safe waste management solutions to major waste generating industries and organisations. The core objectives of value creation, customer service and technical excellence together drive the company’s initiative towards providing sustainable waste management solutions under the brand name – Geocycle. A key challenge posed on environment today that is a cause of major concerns about the health and safety of all citizens comes from the enormous volumes of municipal waste being generated in our cities and towns. Recognising this problem, the company is extending the scope of its waste management solutions to developing safe and sustainable solutions for the efficient disposal of municipal wastes. In the course of providing waste management solutions to municipalities, ACC also seek to reduce reliance on traditional fuels.

ACC has increased co-processing of RDF and non-recyclable SCF of MSW in its facilities enabled by large scale investments in R&D made for the safe utilisation of these waste streams. ACC, in this case, is working with state governments and waste management agencies such as in Goa on a MSW Landfill Remediation Project, the first-of-its-kind project in India, wherein ACC received and co-processed around 4,800 tonnes of RDF at the Wadi plant in 2016.

ACC redoubled its endeavours in lobbying, advocacy and capacity building to achieve greater technical and legal recognition for co-processing technology in line with accepted international standards.

"Banned wastes" not to be pre-processed or co-processed:
Radioactive waste
Asbestos-containing waste
Explosives and ammunition / weapons
Anatomical medical waste

"Banned wastes" not to be co-processed (These wastes however can be co-processed after
pre-processing to remove the banned portion of the waste):
Electronic fraction of electrical and electronic waste (e-waste)
Whole batteries as a targeted material stream
Waste of unknown or unpredictable composition, including unsorted municipal waste

-RAHUL KAMAT

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Concrete

Balancing Demand and Sustainability

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ICR discusses India’s rapid advances in renewable energy, on track to exceed its 2030 targets, even as the rising energy demands challenge complete reliance on sustainable sources.

The cement industry, a cornerstone of infrastructure development, has long been associated with high emissions, particularly of CO2. This sector alone is responsible for approximately 8 per cent of global carbon dioxide emissions, primarily due to the energy-intensive processes of clinker production and calcination. Beyond carbon emissions, cement production also generates particulates, nitrogen oxides (NOx), sulphur oxides (SOx), and other pollutants, contributing to environmental degradation and health risks. With the global push towards sustainable practices and carbon neutrality, addressing emissions in the cement industry has become imperative.
According to Climate Change Performance Index, India ranks 7 in 2024. India receives a high ranking in the GHG Emissions and Energy Use categories, but a medium in Climate Policy and Renewable Energy, as in the previous year. While India is the world’s most populous country, it has relatively low per capita emissions. Data shows that in the per capita GHG category, the country is on track to meet a benchmark of well below 2°C.
India’s situation underscores the complexity of transitioning to sustainable energy systems in the face of rising and fluctuating energy needs. International support is crucial for India to access advanced technologies, financial resources, and best practices that can accelerate its transition to a sustainable energy future. Our analysis shows that with current policies, India will overachieve its conditional NDC targets of achieving 50 per cent non-fossil capacity by 2030, so it could set stronger targets. India has ambitious renewable energy plans as outlined in the National Electricity Plan 2023 (NEP2023) aiming for a share of installed capacity of 57 per cent and 66 per cent in 2026-27 and 2031-32, respectively. Share of renewable energy capacity in India reached 44 per cent, ranked fourth in the world in renewable energy capacity installations in 2023, after China, the US and Germany. The NEP2023 is reflected in the lower bound of our current policy and action pathway.
India has seen a steady increase in renewable energy deployment, including both utility-scale and rooftop solar, leading to the share of coal capacity dropping below 50 per cent for the first time. However, this increase in renewable energy capacity is barely able to keep up with the surging demand. As a result, the electricity generation share of renewable energy, including large hydro, remains at around 18 per cent, showing no improvement since last year. Investment in renewable energy projects in India are projected to increase by over 83 per cent to around USD 16.5 bn in 2024, with fossil fuel companies also diversifying their investments into the renewable sector. Despite this, India has not committed to phasing out coal power or fossil gas.
The National Electricity Plan indicated a temporary halt in coal capacity addition, but current under-construction capacity exceeds the threshold stated in these plans. While new gas power projects have been abandoned, the utilisation of existing gas power plants has increased to meet energy demand driven by severe heat stress.

Understanding Emissions in Cement Production
Primary Sources of Emissions: Cement production emissions stem mainly from three sources: calcination, fuel combustion, and electricity use. During calcination, limestone is heated to produce clinker, releasing CO2 as a by-product. This process alone accounts for roughly 60 per cent of emissions in cement manufacturing. The remaining emissions result from burning fossil fuels in kilns to achieve the high temperatures needed for calcination and from electricity consumption across production stages.
Raju Ramchandran, SVP Manufacturing (Cluster Head – Central), Nuvoco Vistas, says, “We consistently track air emissions from fuel combustion in our cement manufacturing and power generation operations. The burning of fossil fuels releases pollutants such as Oxides of Sulphur (SOx), Oxides of Nitrogen (NOx), and Particulate Matter (PM), which require stringent monitoring.”
“We ensure compliance with regulatory standards by using the Continuous Emission Monitoring System (CEMS) to monitor these emissions. For the FY 23-24, both our stack and fugitive emissions have stayed within the permissible limits set by Pollution Control Boards. Moreover, our ongoing monitoring of fugitive emissions ensures that we meet the prerequisite air quality standards,” he adds.
In addition to CO2, the cement industry releases various pollutants that pose risks to air quality and public health. These include particulate matter, NOx, and SOx, which can lead to respiratory and cardiovascular issues, acid rain, and ecosystem imbalances.
Governments worldwide are setting increasingly stringent regulations to curb industrial emissions. Standards such as the EU Emissions Trading System and India’s National Action Plan on Climate Change encourage cement manufacturers to adopt cleaner technologies. Many countries now impose limits on NOx, SOx and particulate emissions, with the aim of minimising the industry’s environmental impact.

Challenges in Reducing Emissions
High carbon intensity of cement production: Cement’s high carbon intensity largely stems from the chemical reactions involved in transforming limestone into clinker, making emissions difficult to reduce without altering core processes. Additionally, achieving the necessary kiln temperatures requires significant energy, often derived from coal or natural gas.
Operational limitations: Altering the traditional cement production process can compromise the quality and durability of the end product. Adapting existing production lines for lower emissions involves extensive R&D and technical trials to ensure the finished cement meets industry standards.
Financial constraints: The cost of implementing green technology is high, creating economic challenges, particularly for smaller cement manufacturers. Equipment upgrades, energy-efficient kilns, and carbon capture facilities require considerable investment, which many companies find difficult to justify without strong financial incentives.
Balancing market demands and environmental goals: With global infrastructure demands rising, the cement industry faces pressure to meet growing production needs while simultaneously working to reduce emissions. Balancing these competing demands requires innovation, efficient resource management, and support from stakeholders.

Technological Innovations for Emission Reduction
Alternative fuels and energy sources: One of the most effective ways to reduce emissions is by replacing fossil fuels with alternatives like waste-derived fuels, biomass, or biofuels. Some manufacturers are incorporating solar and wind energy to power auxiliary processes, further reducing reliance on traditional energy sources.
Sudhir Pathak, Head- Central Design & Engg (CDE), QA, Green Hydrogen, Hero Future Energies, says, “The cement industry is one of the largest consumers of grid power (Scope 2) and also a guzzler of in-process fossil CO2 (Scopem1) including process-based CO2 through limekilns. Decarbonisation can be achieved only up to 50 per cent to 60 per cent through plain hybrid solar and wind. However, for achieving balance 40 per cent, storage is essential, be it chemical or mechanical. Today, HFE is ready to provide such bespoke storage solutions as is evident through several complex RTC tenders that we have won in the last 6-8 months floated by agencies like SECI, NTPC and SJVN. These include tenders for FDRE projects, peak power, load following, etc. Further, regarding green hydrogen and its derivatives, we are ready to apply these for decarbonising industrial heating and mobility.”
Carbon Capture and Storage (CCS): CCS technology captures emissions at the source, storing CO2 to prevent it from entering the atmosphere. Recent advancements in CCS technology make it a viable option for large-scale cement plants, although high costs and infrastructure requirements remain obstacles to widespread adoption.
Clinker Substitution: Reducing clinker content is a promising method for emission reduction, achieved by using supplementary cementitious materials (SCMs) such as fly ash, slag, and calcined clay. These materials not only reduce CO2 emissions but also enhance the durability and performance of cement. SCMs are gradually becoming industry-standard components, especially in eco-friendly and green cement products.
Rajesh Kumar Nayma, Assistant General Manager – Environment, Wonder Cement, says, “The use of AFR plays a critical role in our strategy to reduce the environmental footprint of cement production. By substituting traditional fossil fuels with waste-derived alternatives like biomass, refuse-derived fuel (RDF) and industrial by-products, we significantly lower CO2 emissions and reduce the demand for natural resources. The utilisation of supplementary cementitious materials (SCMs), such as fly ash, helps in reducing clinker consumption, which is a major source of carbon emissions in cement production. This not only decreases our reliance on energy-intensive processes but also promotes waste recycling and resource efficiency. AFR adoption is an integral part of our commitment to the circular economy, ensuring that we minimise waste and optimise the use of materials throughout the production cycle, ultimately contributing to a more sustainable and eco-friendly cement industry.”
“WCL is exploring transitioning from fossil fuels to cleaner alternatives like biofuels or hydrogen or RDF/plastic waste/other hazardous waste. Till date, 5 per cent TSR has been achieved, while the intent is to achieve more than 20 per cent TSR. WCL is utilising the hazardous and other waste as an alternative fuel or raw material. We have used more than 3 lakh metric tonne of hydrogen waste and other waste in FY-2023-24,” he adds.
Improving energy efficiency is critical for emissions reduction. Technologies like high-efficiency kilns, heat recovery systems, and process optimisation techniques are helping manufacturers achieve more output with less energy. These measures reduce the carbon footprint while lowering operational costs.

The Role of SCMs
SCMs serve as partial replacements for clinker, providing a dual benefit of reduced carbon emissions and improved product resilience. The use of materials like fly ash and slag also helps mitigate industrial waste, contributing to a circular economy. Fly ash, slag, and silica fume are among the most widely used SCMs. Each has unique properties that contribute to cement’s strength, workability, and durability. By incorporating SCMs, manufacturers can produce cement with a lower environmental footprint without compromising quality.
While SCMs are effective, several obstacles hinder their widespread adoption. Supply chain constraints, material variability, and lack of technical standards are challenges that manufacturers face. Additionally, geographic limitations impact access to certain SCMs, creating disparities in their usage across regions.

Policy and Industry Collaboration
Policies play a critical role in driving green transitions within the cement industry. Carbon credits, tax incentives, and funding for R&D are some measures governments have introduced to support emission reduction. India’s Perform, Achieve, and Trade (PAT) scheme is an example of a policy incentivising industrial energy efficiency.
Collaborations between government entities, private corporations, and research institutions foster innovation and accelerate the adoption of sustainable practices. Partnerships can also help address funding gaps, allowing companies to explore new technologies without bearing the full financial burden.
International frameworks such as the Paris Agreement and industry-led efforts like the Global Cement and Concrete Association (GCCA) are setting targets for sustainable cement production. These initiatives encourage the sector to adopt environmentally friendly practices and set a roadmap toward achieving net-zero emissions.

Towards a Net-Zero Future
Reaching net-zero emissions is an ambitious but necessary goal for the cement industry. Realistic targets, set with interim milestones, allow companies to gradually transition to greener processes while maintaining production efficiency. Continued investment in R&D is crucial for discovering new methods of emission reduction. Emerging technologies such as carbon-negative materials, alternative binders, and low-carbon clinkers hold promise for the future, potentially transforming cement production into a more sustainable process.
Increasingly, consumers and investors are prioritising sustainability, placing pressure on companies to reduce their environmental impact. This shift in consumer sentiment is driving the cement industry to adopt green practices and focus on transparency in emissions reporting.

Conclusion
The journey toward reducing environmental impact in the cement industry is complex and multifaceted, requiring a combination of innovation, policy support, and industry collaboration. By adopting alternative fuels, implementing carbon capture technology, integrating SCMs, and improving energy efficiency, the industry can take significant strides in minimising its carbon footprint. Achieving sustainability in cement production is essential not only for the industry’s future but also for the planet’s well-being. Together, industry players, policymakers, and consumers can support the transition to a net-zero future, ensuring that cement remains a vital yet sustainable component of global infrastructure.

– Kanika Mathur

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Concrete

Red River Formation in Kiln Operations

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Dr SB Hegde, Professor, Jain College of Engineering and Technology, Hubli, and Visiting Professor, Pennsylvania State University, USA, helps us understand the red river formation in cement kiln operations, its causes, impacts and mitigation strategies.

Red river formation in cement kilns, where molten clinker flows uncontrollably in the cooler, is a costly problem for cement plants. The phenomenon not only affects clinker quality but also leads to significant operational disruptions, increased energy consumption and accelerated wear on kiln refractory bricks. Understanding the factors that cause red river formation and implementing strategies to prevent it are critical to maintaining operational efficiency and clinker quality.
This paper explores the causes of red river formation, the operational impacts it has on kiln performance, and the various mitigation strategies that cement plants can adopt. Additionally, safety considerations associated with the prevention and handling of red river formation are discussed, with practical insights from case studies of successful plant interventions in India and globally.

Causes of red river formation
Red river formation is primarily caused by improper kiln operations, including fluctuating kiln temperatures, oxygen levels, and cooler inefficiency. The following parameters are essential contributors:
Kiln temperature: Inconsistent temperature control in the kiln’s burning zone, often exceeding 1500°C, creates an imbalance between the solid and molten clinker phases, leading to red river formation. Maintaining temperatures within a more stable range of 1470-1490°C ensures that the clinker remains solid as it moves into the cooler.
Oxygen levels and CO concentrations: Oxygen levels above 2.5 per cent increase the risk of over-combustion, while elevated CO levels above 0.3 per cent indicate incomplete combustion, both contributing to excessive clinker melting. Optimising oxygen levels to 1.8-2.0 per cent minimises the risk.
Raw mix composition: The raw mix plays a vital role in clinker formation. A high liquid phase due to improper ratios of silica, alumina, and iron oxide can lead to excessive melting. Controlling the silica modulus (SM: 2.3-2.7) and alumina modulus (AM: 1.3-1.8) ensures a more stable clinker and reduces the risk of red river formation. If the raw mix is improperly proportioned, red river formation becomes more likely due to high fluxing compounds that melt at lower temperatures.
Kiln speed and torque: Kiln speeds that fluctuate below 3.4 rpm can cause material buildup, while kiln torque exceeding 50-60 per cent indicates stress that can lead to clinker instability.
Cooler efficiency: Inefficiencies in the clinker cooler, with efficiency levels below 78 per cent, can exacerbate red river formation. Clinker that is not cooled properly will remain molten for longer, allowing it to flow uncontrollably. Coolers should maintain exit temperatures between 180-200°C to prevent red river incidents.
Impact on clinker quality and kiln performance
The occurrence of red river has numerous negative impacts on both clinker quality and kiln performance:
Clinker quality: Red river formation results in poor clinker grindability, higher variability in free lime content and inconsistent cement properties. Poor clinker reactivity reduces both early and late strength development in the final cement product.
Increased heat consumption: Red river typically increases specific heat consumption by 3-5 per cent, resulting in higher fuel usage. These inefficiencies can significantly affect the plant’s cost structure, driving up operational expenses.
Refractory damage: The molten clinker accelerates the wear of refractory bricks in the kiln, especially in the burning zone and cooler transition areas. Brick life can decrease by 25-30 per cent, leading to more frequent replacements and higher maintenance costs.
Equipment and instrumentation damage: The uncontrolled molten flow of clinker during red river incidents can damage cooler plates, kiln discharge systems, and even temperature sensors and thermocouples, leading to costly repairs and prolonged downtime.

Mitigation strategies
Mitigating red river formation requires a multi-faceted approach combining operational optimisation, automation and staff training:
Kiln temperature control: Maintaining stable burning zone temperatures in the 1470-1490°C range is key to preventing excessive melting of clinker. Advanced temperature monitoring systems can help regulate temperature fluctuations.
Cooler efficiency optimisation: To ensure proper cooling, cooler efficiency must be maintained at 78-80 per cent, with clinker exit temperatures not exceeding 200°C. Real-time airflow adjustments in grate coolers improve cooling performance, solidifying the clinker at the appropriate stage.
Automation and data analytics: Advanced Process Control (APC) systems using data analytics can monitor critical kiln parameters—such as temperature, oxygen levels, and torque—in real-time, allowing for predictive maintenance and early intervention when red river signs appear. This technology has been implemented successfully in leading plants globally to prevent red river formation.

Indian case studies
Case Study 1: Cement Plant in South India – Optimisation of Kiln Parameters
A cement plant in South India faced recurrent red river issues due to high kiln temperatures and low cooler efficiency. After comprehensive process audits, the plant optimised its kiln temperature to 1480°C, reduced oxygen levels to 1.9 per cent, and upgraded its cooler to an efficiency of 80 per cent. These changes reduced red river incidents by 85 per cent, saving the plant Rs 10 million in energy costs annually and improving clinker quality by
15 per cent.

Case Study 2: Cement Plant in North India – Cooler Upgrade and Automation
A northern India plant increased cooler efficiency from 70 per cent to 78 per cent by installing an advanced grate cooler. This reduced clinker exit temperatures to 190°C, preventing red river formation. Automation systems provided real-time adjustments, decreasing the frequency of incidents by 75 per cent and saving `12 million annually.

Global Case Studies
Case Study 1: European Plant – Automation Success
A German cement plant, experiencing red river issues due to fluctuating oxygen levels, installed an advanced data-driven automation system. The system stabilised oxygen at 1.9 per cent and maintained kiln temperature at 1,475-1,485°C, reducing red river by 90 per cent. Clinker quality improved by 10 per cent, with a reduction in specific heat consumption by 4 per cent.

Case study 2: US Plant – Operator Training and Process Optimisation
A US cement plant reduced red river occurrences by 70 per cent through kiln speed optimisation (3.8 rpm) and comprehensive operator training. Improved monitoring of kiln torque and cooler exit temperatures led to higher cooler efficiency (75 per cent) and an annual savings of $2 million.

Safety Aspects
Safety is a paramount concern in red river incidents. When molten clinker flows uncontrollably, it poses a significant risk to personnel working near the kiln and cooler areas.

To mitigate these risks:

  • Clearance zones: Kiln and cooler areas should have strict clearance zones for personnel when red river incidents are detected.
  • Protective gear and training: Personnel should be equipped with proper protective equipment (PPEs) and trained to handle emergencies involving molten clinker. Emergency shutdown procedures should be well-documented and rehearsed.
  • Automation and early warning systems: Automation can provide early warning systems that alert operators to potential red river formation before it becomes critical, ensuring safe intervention.

Conclusion
Red river formation remains a major operational challenge for cement plants, but it can be effectively mitigated through proper kiln temperature control, cooler efficiency optimisation and the use of advanced automation systems.
The case studies highlight the importance of process improvements and staff training in reducing red river occurrences, improving clinker quality, and lowering operational costs. Additionally, safety
measures must be prioritised to protect personnel from the risks posed by molten clinker. By incorporating these strategies, cement plants can ensure consistent kiln performance and enhanced operational efficiency.

References
1. Duda, W. H. (1985). Cement Data Book. International Process Engineering in the Cement Industry. Bauverlag GmbH.
2. Javed, I., & Sobolev, K. (2020). “Use of Automation in Modern Cement Plants.” Cement and Concrete Research, 130, 105967.
3. Tamilselvan, P., & Kumar, R. (2023). “Optimisation of Kiln and Cooler Systems in Indian Cement Plants.” Indian Cement Review, 34(7), 42-48.
4. Martin, L. (2019). “Case Studies of Red River Mitigation in European Cement Plants.” International Journal of Cement Production, 12(2), 63-78.
5. Schorr, H. (2021). “Advanced Process Control in Cement Manufacturing.” Cement International, 19(3), 30-37.
6. Singh, V. K., & Gupta, A. (2022). “Impact of Raw Mix on Clinker Formation and Kiln Operations.” Global Cement Magazine, 14(4), 22-29.

About the author: Dr SB Hegde brings over thirty years of leadership experience in the cement industry in India and internationally. He has published over 198 research papers and holds six patents, with four more filed in the USA in 2023. His advisory roles extend to multinational cement companies globally and a governmental Think Tank, contributing to research and policy. Recognised for his contributions, he received the ‘Global Visionary Award’ in 2020 from the Gujarat Chambers of Commerce and Industry.

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SCMs encourage closed-loop systems

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As the cement industry prioritises sustainability and performance, Supplementary Cementitious Materials (SCMs) are redefining standards, explains Tushar Khandhadia, General Manager – Production, Udaipur Cement Works.

What role do supplementary cementitious materials (SCMs) play in enhancing the performance and sustainability of cement and concrete?
SCMs play a crucial role in enhancing the performance and sustainability of cement and concrete. These materials are added to concrete to improve its properties such as strength, durability, and workability, as well as to reduce the environmental impact of cement production. The addition of SCMs to cement reduces the amount of Portland cement required to manufacture concrete, reducing the carbon footprint of the concrete. These materials are often industrial waste products or by-products that can be used as a replacement for cement, such as fly ash, slag and silica fume.
SCMs also reduce the amount of water required to produce concrete, which reduces the environmental impact of concrete production. This is achieved through their ability to improve the workability of concrete, allowing the same amount of work to be done with less water.
In addition, SCMs improve the durability of concrete by reducing the risk of cracking and improving resistance to chemical attack and other forms of degradation.

How has your company integrated SCMs into its production process, and what challenges have you encountered?
The integration of SCMs into cement and concrete production may pose certain challenges in the areas of sourcing, handling and production optimisation.

  • Sourcing: Finding an adequate and reliable supply of SCMs can be a challenge. Some SCMs, such as fly ash and slag, are readily available by-products of other industrial processes, while others such as silica fume or metakaolin may be more difficult to source.
  • Handling: The storage, handling, and transportation of SCMs require special considerations due to their physical and chemical properties. For instance, some SCMs are stored in moist conditions to prevent them from drying out and becoming airborne, which could pose a safety risk to workers.
  • Production optimisation: The addition of SCMs into the mix may require adjustments to the production process to achieve the desired properties of cement and concrete. For example, the use of SCMs may affect the setting time, workability, strength gain, and other properties of the final product, which may require reconfiguration of the production process.
  • Quality control: The addition of SCMs may introduce variability in the properties of cement and concrete, and rigorous quality control measures are necessary to ensure the final product meets the required specifications and standards.

Proper planning, handling and production optimisation are essential in overcoming the challenges encountered during the integration process.

Can you share insights on how SCMs such as fly ash, slag and silica fume impact the durability and strength of concrete in different environmental conditions?

  • Fly ash is a by-product of coal combustion and is widely used as an SCM in the production of concrete. When added to concrete, fly ash reacts with the calcium hydroxide present in the concrete to form additional cementitious materials, resulting in improved strength and durability. Fly ash increases the durability of concrete by improving its resistance to sulphate and acid attacks, reducing shrinkage and decreasing the permeability of concrete. Fly ash also enhances the workability and pumpability of concrete while reducing the heat of hydration, which reduces the risk of thermal cracking. In cold climates, fly ash helps to reduce the risk of freeze-thaw damage.
  • Slag is a by-product of steel production and is used as an SCM because of its high silica and alumina content. When added to concrete, slag reacts with the calcium hydroxide present in the concrete to form additional cementitious materials, resulting in improved strength and durability. Slag increases the durability of concrete by improving its resistance to sulphate and acid attacks, reducing shrinkage and improving the strength of concrete over time. Slag also enhances the workability of concrete, reduces the heat of hydration, and improves the resistance of concrete to chloride penetration.
  • Silica fume is a by-product of the production of silicon and ferrosilicon alloys and is used as an SCM because of its high silica content. When added to concrete, silica fumes react with the calcium hydroxide present in the concrete to form additional cementitious materials, resulting in improved strength and durability. Silica fume increases the durability of concrete by improving its resistance to sulphate and acid attacks, reducing permeability, and improving abrasion resistance. Silica fume also enhances the workability of concrete, reduces the heat of hydration, and improves the resistance of concrete to chloride penetration.

Overall, the use of SCMs such as fly ash, slag and silica fume can significantly improve the durability and strength of concrete in different environmental conditions. Their impact on concrete varies depending on the availability, physical and chemical properties of the specific SCM being used and proper testing and engineering analysis should be done for each mix design in order to optimise the final product.

With the global push for sustainability, how do SCMs contribute to reducing the carbon footprint of cement production?
SCMs provide an environmentally friendly alternative to traditional Portland cement by reducing the amount of clinker required to produce cement. Clinker is the main ingredient in Portland cement and is produced by heating limestone and other raw materials to high temperatures, which releases significant GHG emissions. Thus, by using SCMs, less clinker is required, thereby reducing GHG emissions, energy use and the environmental impact of cement production. Some SCMs such as fly ash and slag are by-products of other industrial processes, meaning that their use in cement production reduces waste and enhances resource efficiency. Moreover, the use of SCMs can enhance the properties of concrete, thereby increasing its durability and service life which helps to further reduce the overall embodied carbon of the structure.
In short, the use of SCMs contributes to reducing the carbon footprint of cement production by improving the efficiency of resource utilisation and reducing greenhouse gas (GHG) emissions during the production process. This has led to an increased demand for SCMs in the construction industry, as environmental concerns and sustainable development goals have become more prominent factors in the selection of building materials.

What strategies or innovations has your company adopted to ensure a consistent and reliable supply of SCMs, given their reliance on industrial by-products?

  • Developing partnerships with suppliers: Many cement and concrete manufacturers establish long-term partnerships with suppliers of SCMs. These partnerships provide a reliable supply of high-quality SCMs, improve supply chain efficiency, and often provide access to new sources of SCMs.
  • Advanced SCM processing techniques: Many companies are investing in advanced processing techniques to unlock new sources of high-quality SCMs. Advanced processing techniques include new separation processes, calcination techniques, and chemical activation methods.
  • Alternative SCM sources: Many companies are exploring alternative SCM sources to supplement or replace traditional SCMs. Examples include agricultural by-products such as rice hull ash or sugar cane bagasse ash, which can be used in place of fly ash.
  • Quality control measures: Strict quality control measures are necessary to ensure consistent quality of SCMs. Many companies use advanced testing methods, such as particle size analysis, chemical analysis, and performance testing, to validate the quality of SCM materials used in production.
  • Supply chain diversification: Diversifying suppliers and SCM sources is another way to ensure a reliable supply. This reduces the risk of supply chain disruptions caused by factors such as natural disasters, market changes, or geopolitical risks.

The strategies and innovations adopted to ensure a consistent and reliable supply of SCMs include establishing long-term partnerships with suppliers, investing in advanced processing techniques, exploring alternative SCM sources, implementing strict quality control measures, and diversifying supply chains. By implementing these approaches, we ensure that use of SCMs in cement production is an effective and viable solution for reducing the environmental impact of operations

How does the use of SCMs align with your company’s broader goals around circular economy and resource efficiency?
Here are some ways in which the use of SCMs supports these goals:

  • Reducing waste: The use of SCMs, such as fly ash and slag, diverts significant quantities of industrial waste from landfills, turning it into a valuable resource that can be used in construction. This helps to reduce waste and conserve natural resources.
  • Reducing carbon emissions: Cement production is a significant contributor to greenhouse gas emissions, and the use of SCMs can significantly reduce the amount of cement required in concrete mixtures. This helps to reduce the carbon footprint of construction activities and move towards a low-carbon economy.
  • Enhancing resource efficiency: The use of SCMs can reduce the demand for raw materials, energy, and water in the production of concrete. This not only conserves natural resources but also reduces the costs associated with the extraction, transportation and processing of these materials.
  • Closing the loop: SCMs encourage closed-loop systems in the construction sector, where waste materials from one process become input materials for another. This can improve the efficiency and sustainability of the construction industry.
  • Supporting sustainable design practices: The use of SCMs can support sustainable design practices by improving the durability and performance of structures while also reducing their environmental impact. This supports a circular approach to design, construction and operation of buildings and infrastructure
    that improves their social, economic and environmental sustainability.

What future trends or developments do you foresee in the use of SCMs within the cement industry?
Future trends in the use of SCMs within the cement industry are likely to focus on: increased utilisation of diverse waste-derived SCMs, development of new SCM sources to address potential shortages, advanced characterisation techniques to optimise SCM blends and data-driven approaches to predict and optimise SCM usage for reduced carbon footprint and improved concrete performance; all driven by the growing need for sustainable cement production and stricter environmental regulations.
Key aspects of this trend include:

  • Expanding SCM sources: Exploring a wider range of industrial byproducts and waste materials like recycled concrete aggregate, activated clays and certain types of industrial minerals as potential SCMs to reduce reliance on traditional sources like fly ash, which may become increasingly limited.
  • Advanced material characterisation: Utilising sophisticated techniques to better understand the chemical and physical properties of SCMs, allowing for more precise blending and optimisation of their use in cement mixtures.
  • Data-driven decision making: Implementing machine learning and big data analysis to predict the performance of different SCM combinations, allowing for real-time adjustments in cement production based on available SCM sources and desired concrete properties.
  • Focus on local sourcing: Prioritising the use of locally available SCMs to reduce transportation costs and environmental impact.
  • Development of new SCM processing techniques: Research into methods to enhance the reactivity and performance of less readily usable SCMs through processes like activation or modification.
  • Life cycle analysis (LCA) integration: Using LCA to assess the full environmental impact of different SCMs and optimise their use to minimise carbon emissions throughout the cement production process.
  • Regulatory frameworks and standards:Increased adoption of building codes and industry standards that promote the use of SCMs and set targets for reduced carbon emissions in cement production.

– Kanika Mathur

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