Environment
Fly ash utilisation in Samruddhi Mahamarg
Published
6 years agoon
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admin
Maharashtra Government has undertaken an ambitious project, the first-of-its-kind (distance wise) in the country. The project has a big potential of using fly ash as a construction material. A glimpse of the project has been compiled by Sudhir Paliwal and Dr Ajitkumar Bhonsle.
Mumbai Nagpur Super Communication Expressway-also known as Maharashtra Samruddhi Mahamarg under construction-is a 701 km long, six-lane expressway, connecting the two capitals of Maharashtra – Nagpur and Mumbai. The expressway will run through 10 districts, 26 tehsils, and 390 villages in the State, and is expected to cut travel time between the two cities to eight hours. The project is expected to cost Rs 46,000 crore and requires the acquisition of 8,603 hectares of land.
The Maharashtra State Road Development Corporation is the nodal agency responsible for executing the project, which comprises building a completely greenfield expressway, designed for speeding up to 150 km/h on flat terrain and up to 100 km/h on the mountainous terrain of the Western Ghats section. The State Government also plans to build 24 townships along the route, which will include state-of-the-art healthcare facilities, skill management centres, IT parks and educational institutions. A total of 20,820 hectares of land is to be acquired for the project across 10 districts, out of which 8,520 hectares will be used for the highway, while 10,800 hectares would be for building townships.
The aim of the super communication expressway is to create connectivity to the last mile with best public transport facilities for quick and easy movement of people and goods. The expressway will enable a large population to have easy access to major centres in Maharashtra for a wide range of self-employment and wage employment opportunities, business, trade, education, health care and other necessary services.
Samruddhi Mahamarg Expressway
The expressway will pass through 10 districts, namely Nagpur, Wardha, Amravati, Washim, Buldhana, Aurangabad, Jalna, Ahmednagar, Nashik and Thane. It will connect Nagpur to Mumbai and have direct connectivity with the country’s largest container port – JNPT. This will enhance export-import trade of the State. Inter-connecting highways and feeder roads would be constructed to connect all important cities and tourist places along this route. This will connect another 14 districts, namely Chandrapur, Bhandara, Gondia, Gadchiroli, Yavatmal, Akola, Hingoli, Parbhani, Nanded, Beed, Dhule, Jalgaon, Palghar and Raigad. In this manner, a total of 24 districts in Maharashtra will be connected via this expressway.
Major tourist destinations in the State will also be connected to the expressway. The expressway, having a total width of 120 m with a central median of 22.5 m, will follow the international standards of design. There will be eight lanes, four on each side. In case there is a need to increase lanes on either side, a provision has been made in the centre of the expressway. Thus, no more land will be required for expansion in future. It will have service roads on both sides that will connect through underpasses.
The expressway will have around 50+ flyovers, 24+ interchanges, over five tunnels, 400+ vehicular and 300+ pedestrian underpasses provided at strategic locations. These underpasses and flyovers will be beneficial to those vehicles leaving or joining the expressway without disturbing the traffic flow. It will also benefit local citizens to go about their travel without any hindrance and also prevent accidents.
Extensive landscaping, tunnel lighting, bridge beautification, improved street lighting and digital signage will be used throughout the length of the expressway. Maximum locally available material, fly ash and plastic will be used to construct the expressway wherever possible. Rainwater will also be harvested from the expressway. The entry and exit at the expressway will be managed and toll will be charged based on the distance travelled. The toll collection is proposed to be automated. The expressway will be a Zero Fatality Mahamarg; it will have CCTV surveillance and free telephone booths at every 5 km to allow reporting in case of any accidents and emergencies. Utility Mahamarg along the expressway will be provided for OFC cables, gas pipelines, electricity lines, etc.
In case of any emergency, natural disaster or in a war-like situation, a facility to land an airplane on the expressway is proposed by temporarily converting the expressway to a runway. The Maharashtra Samruddhi Mahamarg will link the State of Maharashtra to the Delhi-Mumbai Industrial Mahamarg and the Western Dedicated Freight Mahamarg. Parts of Maharashtra will have direct connectivity to these Mahamarg and JNPT, the country’s largest container port. This, in turn, will enhance the EXIM trade of the State.
Advantages of using fly ash
The Indian Roads Congress (IRC) guidelines IRC:SP:58-2001 provide salient details regarding design and construction of road embankments using fly ash. Utilisation of fly ash will not only minimise the disposal problem but will also help in utilising precious land in a better way. Construction of road embankments using fly ash, involves encapsulation of fly ash in earthen core or with RCC facing panels. Since there is no seepage of rainwater into the fly ash core, leaching of heavy metals is also prevented. When fly ash is used in concrete, it chemically reacts with cement and reduces any leaching effect. Even when it is used in stabilisation work, a similar chemical reaction takes place, which binds fly ash particles. Hence chances of pollution due to use of fly ash in road works are negligible.
Fly ash is a lightweight material, as compared to commonly used fill material (local soils), therefore, causes lesser settlements. It is especially attractive for embankment construction over weak subgrade such as alluvial clay or silt where excessive weight could cause failure.
Fly ash embankments can be compacted over a wide range of moisture content, and therefore, results in less variation in density with changes in moisture content. Easy to handle and compact because the material is light and there are no large lumps to be broken down. Can be compacted using either vibratory or static rollers.
High permeability ensures free and efficient drainage. After rainfall, water gets drained out freely ensuring better workability than soil. Work on fly ash fills/ embankments can be restarted within a few hours after rainfall, while in case of soil it requires much longer period.
Considerable low compressibility results in negligible subsequent settlement within the fill.
Conserves good earth, which is precious topsoil, thereby protecting the environment.
Higher value of California Bearing Ratio as compared to soil provides for a more efficient design of road pavement.
Pozzolanic hardening property imparts additional strength to the road pavements / embankments and decreases the post construction horizontal pressure on retaining walls.
Amenable to stabilisation with lime and cement.
Can replace a part of cement and sand in concrete pavements thus making them more economical than roads constructed using conventional materials.
Fly ash admixed concrete can be prepared with zero slump making it amenable for use as roller compacted concrete.
Considering all these advantages, it is extremely essential to promote use of fly ash for construction of roads and embankments.
Use of fly ash in road works results in reduction in construction cost. If environmental degradation costs due to use of precious top soil and aggregates from borrow areas quarry sources and loss of fertile agricultural land due to ash deposition, etc. is considered the actual savings achieved are much higher.
Govt initiatives for fly ash utilisation in roads
Use of fly ash is mandatory in Road construction: As per para 5 of MoEF&CC notification dated November 3, 2009 – "No agency, person or organisation shall, within a radius of 100 km of thermal power plant undertake construction or approve design for construction of roads or fly-over embankment with TOP SOIL."
As per the para No.2 (14) of MOEF&CC notification dated January 25, 2016 – "The coal or lignite based thermal power plants shall within a radius of three hundred kilometres bear the entire cost of transportation of ash to the site of road construction projects under Pradhan Mantri Gramin Sadak Yojna and asset creation programmes of the Government involving construction of building, road, dams and embankments.
Maharashtra State has notified Ash Utilisation Policy – 2016 and constituted Maharashtra State Fly Ash Council under the Chairmanship of Chief Secretary, Maharashtra. As per the State ash policy, point No. 1, 2 & 3 under para "Government Decisions", – "fly ash to be transported free of cost for Government infrastructure projects, roads construction by the ash producers i.e. thermal power plants"
In compliance of MoEF&CC notifications NTPC has been issuing ash free of cost for road construction projects and also entering in to MoU with NHAI for bearing transportation cost of ash. More than 100 lakh tons of Fly Ash is utilised in NHAI projects in Maharashtra and other States where fly ash is generated.
Samruddhi Mahamarg between Nagpur and Mumbai is passing within 300 km radius of several power plants like Reliance Butibori, Ideal Energy, Mahagenco Khaprkheda/Koradi, NTPC Mouda, Ratan India Amraoti, Mahgenco Paras, Bhusawal, Parli & Nasik, Tata Power, Adani Power, etc.
The Ministry of Road Transport & Highways, Government of India also issued following directions wide letter dated August 27, 2018: The use of fly-ash in road construction is permitted as per the standards and specifications evolved by the Indian Road Congress. The physical and chemical properties of fly ash and the design methodology to be adopted for embankment construction has been specified in IRC:SP:58:2001: "Guidelines for use of fly-ash in road construction". Section 305 i.e. "Embankment Construction" of MoRT&H specifications for road and bridge works lays down the specifications for use of fly-ash in embankment construction.
Compliance to IRC specification No.SP:58 of 2001 related to use of fly ash has been made mandatory by the Ministry of Environment Forests & Climate Change by issuing an amendment to their fly ash notification while undertaking construction or approve design for construction of roads or flyover embankment.
The Ministry of Environment Forests and Climate Change (MoEF&CC) has issued various notifications for fly ash utilisation. The principal notification was issued on 14-9-1999, which was subsequently amended vide notifications dated 27-8-2003, 3-11-2009 and 25-1-2016. As per the notification of MoEF&CC, it is mandatory to use fly ash in the construction of road or flyover embankments within a radius of 300 km of a thermal power plant. Further, the relevant content of the notification dated 25-1-2016 of MoEF&CC regarding road/ flyover embankment construction are as under:
Para 14: The coal or lignite based thermal power plants shall within a radius of three hundred kilometers bear the entire cost of transportation of ash to the site of road construction projects under Pradhan Mantri Gramin Sadak Yojana and asset creation programmes of the Government involving construction of buildings, road, dams and embankments.
The issue of lesser off-take of fly-ash in road construction activities of the Ministry of Road Transport & Highways and its executing agencies (NHAI, State PWDs and NHIDCL) has been reviewed at the level of the Ministry. It was pointed out that the thermal power plants have been found to be reluctant to bear the transportation costs in accordance with the latest notification issued by the MoEF&CC on the subject. Accordingly Secretary, MoRTH took up the matter with the Secretary, Ministry of Power and the CMD of National Thermal Power Corporation (NTPC). The CMD of NTPC clarified that they had already issued instructions in this behalf to the officers-in- charge of all the NTPC plants. The availability of fly ash at various stations of NTPC is available at NTPC official web site www.ntpc.co.in under the tab "Ash Availability". The names of responsible persons along with telephone number/mobile number/e-mail address to communicate for issues of pond ash are mentioned. The same is also available in the app "ASHTRACK" launched by the Ministry of Power.
As per the Central Electricity Authority during 2017-18 about 196 million tonnes of fly ash was generated in India out of which only 131 million tonne could be utilised. However in roads and flyovers only 6.67 million tonne is utilised, which is just 3.4 per cent of total utilisation.
There is huge potential of utilisation of fly ash in roads like Samruddhi Mahamarg. Use of fly ash is mandatory in road construction: As per para 5 of MoEF&CC notification dated November 3, 2009 – "No agency, person or organisation shall, within a radius of 100 km of thermal power plant undertake construction or approve design for construction of roads or fly-over embankment with top soil."
As per the para No.2 (14) of MOEF&CC notification dated January 25, 2016 – ?The coal or lignite based thermal power plants shall within a radius of three hundred kilometres bear the entire cost of transportation of ash to the site of road construction projects under Pradhan Mantri Gramin Sadak Yojna and asset creation programmes of the Government involving construction of building, road, dams and embankments".
In compliance of MoEF&CC notifications NTPC has been issuing ash free of cost for road construction projects and also entering in to MoU with NHAI for bearing transportation cost of ash. More than 100 lakh tonne of fly ash is utilised in NHAI projects in Maharashtra and other States where fly ash is generated.
Samruddhi Mahamarg between Nagpur and Mumbai is passing within 300 km radius of several power plants like Reliance Butibori, Ideal Energy, Mahagenco Khaprkheda/Koradi, NTPC Mouda, Ratan India Amraoti, Mahgenco Paras, Bhusawal, Parli & Nasik, Tata Power, Adani Power, etc.
In the meeting of Maharashtra State Fly Ash Council held under Chairmanship of Chief Secretary in March 2018, MSPGCL and PWD were directed to sign MOU for fly ash utilisation for Samruddhi Mahamarg.
"In December 2018, an agreement was signed between Maharashtra State Power Generation Company and Nagpur Mumbai Super Communication Expressway to utilise about 300 lakh tonnes of pond ash and 15 lakh tonnes of dry fly ash for entire 700 km road.
ABOUT THE AUTHORs: Sudhir Paliwal is an Expert Member of the Maharashtra State Fly Ash Council Mumbai.
He can be contacted on: 8291089301. Dr Ajitkumar Bhonsle is an expert and advisor on use of fly ash. He can be contacted on: 9821127987
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Procyon Mukherjee discusses the importance of the thermal substitution rate in the use of alternative fuels in the first part of this two-part series.
It was 22nd October 2019, and we were in Wuhan, visiting the world’s largest kiln that was being installed with the design-TSR of 60 per cent, which meant from the inception the system would be ready to take in higher quantity of RDF, largely from the municipal wastes generated at Wuhan. The overall schema included several co-processing units near Wuhan and then the eventual logistics of moving them through barges on the Yangtse river and then through pipelines into the different sections of the kiln and the pre-heater. We were quite astonished to see that it was the municipality of Wuhan who came forward with the entire scheme including logistics that helped the setting up of the plant – essentially a means for incineration of the entire municipal waste of Wuhan.
The rest of the world may not have such a denouement, rather a step-by-step approach of increasing the TSR, with more and more usage of alternate fuels. Thus, in most cases it is an incremental approach, the investments included. It is worthwhile to look at the journey of alternate fuel usage in cement kilns across the world over the last three decades and what are some of the critical investment pathways for increasing TSR.
The first major use of alternative fuels in the cement manufacturing industry emerged during the mid-1980s. The primary goal in substituting fossil fuels was to enable the industry to remain economically competitive, as fuel consumption accounts for almost one-third of the cost of producing clinker. Any positive impact on the environment was considered an added benefit. Since then, there has been increasing sensitivity to the environmental impact of human and industrial activities. Beyond the cost-cutting benefits of alternative fuels, use of these fuels can contribute greatly to the environmentally sound disposal of waste and to the mitigation of greenhouse-gas emissions (GHG).
Therefore, key cement players started to consider alternative fuels as a lever to improve their contribution to sustainable development and as a key component of corporate social responsibility.
The data in the bracket is the current number for TSR. The obvious case in point is the stratospheric increase in TSR rates in Poland. This needs some discussion. The case study on Poland throws some pointers as to how the journey from zero to 88 per cent has been achieved. The notable steps have been:
1. The willingness of Polish cement companies to reduce their operating costs by quickly replicating the alternative fuel experience of international cement groups
2. The enforcement of Polish waste regulations in order to conform to relevant European
Union directives, namely the Waste Framework Directive, the Waste Incineration Directive and the Landfill Directive.
The second one is one of the fundamental reasons to drive the use of alternate fuel. The journey had its humble beginnings with a small state tax imposed on land fill waste (which was collected from the same people who produced the waste) and then the increase of this tax over time, with the transfer of responsibility of waste collection to the land fill operators. Parallelly the ‘extended producer responsibility’ sparked off the implementation of the first waste shredding line to produce refuse-derived fuel (RDF).
In 2005, Germany adopted a ban on the landfilling of recyclable and organic waste, leading to overproduction of RDF. Poland’s shift toward alternative fuel development based on RDF was thus supported by importation of the fuel from Germany for five years, before Germany increased its own waste burning capacity. At that point, the alternative fuel substitution rate in Poland reached 20 percent. In 2008, the state tax was increased sharply, climbing from €4 per tonne in 2007 to about €17 per tonne, with a further doubling announced within the next 10 years. The enforcement of this tax for municipal waste incited waste management companies to invest in alternative solutions.
At that point, shredding line operators were sourcing waste from the industrial sector (obtaining good-quality waste for a low gate fee) as well as from the municipal waste sector, with large cities being the main providers. The extension of sourcing to include municipal waste resulted in a degree of downgrading of RDF quality, but the cement sector continued the effort and pushed the substitution rate to 40 per cent in 2010.
Once the capacity of RDF production lines reached an equilibrium with the alternative fuel capacity of cement plants, the cement companies were able to pressure RDF producers to further improve the fuel quality. To face this new demand, RDF producers had to innovate, improving the quality of the RDF significantly through better sorting and drying sequences (thermal or biological). In parallel, the cement plants developed new tools to improve drying, such as by installing thermal dryers that used the waste heat from the kilns. A new increase to the state tax then put more waste on the market—and at a better price—confirming the trend toward alternative fuel use.
But the crucial area of investment remained how to arrest the pitfalls of high RDF usage in the kilns as there were issues around chlorine, kiln operational stability, enabling the efficient use of diverse and often challenging fuel types, integration of the system with usage of multiple fuels including diverse alternate fuels and monitoring and control. It is in this regard that several specific investments had to be targeted. The lead in this was taken by Germany and followed by all others to see how increase in thermal substitution rates did not come in the way of either impacting the efficiencies or the environment and efforts were directed to create not only a balance but a way to get to 100 per cent of alternate fuel usage, virtually paving the way for 100 per cent TSR.
Some of the most commonly used alternative fuels in the cement industry are biomass, industrial and domestic waste materials, scrap tires, and sewage sludge. The high temperatures, long residence times, and alkaline environment in the cement kiln can prevent the formation of hazardous volatile compounds, making it a suitable option for co-processing waste materials as alternative fuels during cement production. Although the substitution of fossil fuels such as coal and pet coke with alternative fuels can potentially reduce total CO2 emissions from the cement industry, the reduction potentials are often marginal (in the range of 1- 5 per cent for most cases and up to 18 per cent of current CO2 emissions in a few cases) and depend on the source of biogenic emissions. Moreover, due to higher concentrations of sulphur, nitrogen, chlorine, heavy metals, or other volatile matter in some alternative fuels, co-processing can increase emissions of non-CO2 air pollutants of concern in some cases. Thus, an eye on not increasing the emissions (not just CO2 but also SOX and NOX) became a priority. This required investments over time as the RDF usage increased.
Let us see some of these investments in details, like Chlorine By-Pass, Rotating Hot Disc, ID Fan Modification, ESP Fan Modification, etc would be needed the moment the TSR rates would be approaching plus 30 per cent:
1. Chlorine by-pass: This investment is directed at mitigating and protecting a number of
things like:
Managing chlorine build-up
– Alternative fuels like waste-derived fuels often contain high levels of chlorine. This can lead to an accumulation of alkali chlorides in the kiln system.
– Chlorine build-up can cause operational problems, such as the formation of buildups or rings in the kiln and preheater systems, disrupting the material flow and reducing efficiency.
Improving kiln operation stability: High chlorine content can lead to corrosion and fouling of equipment. By removing excess chlorine, the system operates more stably and with fewer maintenance interruptions.
Protecting product quality: Excess chlorine can impact the clinker quality, leading to undesirable properties in the cement. The bypass system helps maintain consistent and high-quality clinker production.
Facilitating use of diverse fuels: Many alternative fuels, such as municipal solid waste, industrial waste, or tires, are economical but contain high chlorine levels. The bypass system enables cement plants to use these fuels without compromising efficiency
or quality.
Reducing environmental impact: Chlorine in the kiln system can lead to the formation of dioxins and furans, which are harmful pollutants. By extracting chlorine from the system, the bypass reduces the risk of these emissions.
How the system works:
The chlorine bypass system extracts a portion of the kiln gas from a specific point (often the kiln inlet) where the alkali chlorides are in a gaseous form. These gases are cooled rapidly to condense and separate the chlorides, which are then collected and disposed of appropriately.
There are eight components of the system:
Gas extraction system
- Function: Extracts a portion of kiln gases from a strategic location, typically near the kiln inlet where volatile alkali chlorides are in gaseous form.
Key components:
– Gas ducts with high-temperature resistance.
– Dampers to control the volume of extracted gas.
Rapid cooling system
- Function: Quickly cools the extracted hot gases to condense alkali chlorides and other volatiles, preventing them from recirculating into the kiln system.
- Key components:
– Water sprays or air quenching systems for
rapid cooling.
– Heat exchangers, if heat recovery is integrated.
Cyclones or bag filters
- Function: Separates condensed alkali chlorides and dust from the cooled gas stream.
- Key components:
– High-efficiency cyclones for coarse particle separation.
– Bag filters or electrostatic precipitators for fine particle removal.
Disposal system for collected byproducts
- Function: Safely manages and disposes of extracted chlorides and dust.
Key components:
– Conveyors or pneumatic transport systems.
– Silos or containment units for storage before disposal.
Bypass gas cooling and conditioning system
- Function: Further conditions the bypass gas before reintegration into the system or venting.
- Key components:
– Cooling towers or gas conditioning towers.
– Water injection systems for temperature control.
Control and automation system
- Function: Monitors and optimises the bypass system to ensure it operates efficiently and safely.
- Key components:
– Sensors for temperature, pressure, and chlorine content.
– Programmable logic controllers (PLCs) for real-time adjustments.
Heat recovery system (optional)
- Function: Captures waste heat from the bypass gases for use in other processes, improving energy efficiency.
- Key components:
– Heat exchangers.
– Steam generators or preheaters.
Integration with main kiln system
- Function: Ensures that the bypass system operates in harmony with the kiln process without disrupting clinker production or fuel efficiency.
- Key components:
– Ducts and valves for gas reintegration or venting.
– Interfaces with kiln control systems.
2. Combustion chamber hot disc
The installation of a combustion chamber (hot disc) in cement kilns for alternate fuel installations serves several critical purposes, enabling the efficient use of diverse and often challenging fuel types. Here’s a breakdown of its key roles:
Efficient combustion of alternative fuels
- The hot disc provides a dedicated zone for the complete combustion of alternate fuels, including those with varying calorific values, moisture content, and particle sizes.
- This ensures that even low-grade or coarse fuels (e.g., tires, municipal solid waste, biomass, or industrial waste) can be burned effectively.
Improved heat transfer
- The combustion chamber is designed to optimise heat generation and transfer, supplying the kiln with the necessary thermal energy.
- It reduces reliance on primary fossil fuels like coal or petcoke, lowering operating costs.
Reduced emissions
- Proper combustion in the hot disc minimises the release of harmful emissions, such as carbon monoxide (CO), volatile organic compounds (VOCs), and unburned hydrocarbons.
- This helps the cement plant meet environmental regulations and sustainability goal
- Enhanced kiln operation stability
- Burning alternative fuels in the combustion chamber isolates their impact from the main kiln, ensuring stable temperatures and operation within the kiln.
- It minimises disruptions caused by the inconsistent burning behaviour of alternative fuels.
Handling difficult fuels
- The hot disc is specifically designed to process fuels that are challenging to handle in the main kiln or calciner, such as large solid fuels (e.g., tires or large biomass pieces).
- The chamber’s design accommodates prolonged fuel residence time and high temperatures, ensuring complete combustion.
Optimised energy efficiency
- By burning alternate fuels close to the kiln inlet or calciner, the hot disc provides pre-heated gases to the kiln system, improving energy efficiency.
- It contributes to a more uniform temperature profile, enhancing clinker quality.
Increased use of waste-derived fuels
- Many cement plants aim to increase their Thermal Substitution Rate (TSR)—the percentage of energy derived from alternative fuels. The hot disc facilitates this transition by enabling higher volumes and more diverse types of alternate fuels to be used safely and efficiently.
Overall benefits
The hot disc system allows cement plants to:
- Reduce dependency on fossil fuels
- Lower operational costs
- Improve sustainability by using waste as a resource
- Comply with stricter environmental regulations.
Rotating hot disc
- Function: The central component where alternative fuels, such as coarse solids (e.g., tires, plastics, or biomass), are introduced and combusted.
Key features:
- Rotating design for even fuel distribution.
– High-temperature resistance to handle intense combustion conditions.
– Adjustable speed to optimise fuel combustion time and efficiency.
Fuel feed system
- Function: Delivers alternative fuels to the hot disc in a controlled manner.
- Key components:
– Conveyors, pneumatic systems, or screw feeders for fuel transport.
– Chutes or injection systems for precise fuel placement.
– Hoppers or silos for storage of alternate fuels before feeding.
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4 weeks agoon
February 12, 2025By
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Rajesh Kumar Nayma, Associate General Manager – Environment and Sustainability, Wonder Cement, in conversation with Kanika Mathur about CCUS technology.
Wonder Cement Limited (WCL), a leading player in the cement industry, is committed to sustainable practices and innovation in its operations. Rajesh Kumar Nayma, Associate General Manager – Environment and Sustainability at WCL, shares insights into the company’s efforts to integrate Carbon Capture, Utilisation, and Storage (CCUS) technology to combat climate change. Through advanced processes and renewable energy initiatives, WCL is paving the way for a greener cement industry.
How is your company incorporating CCUS technology into its operations to promote sustainability?
To combat climate change and achieve Net Zero emissions by 2060, Carbon Capture, Utilisation, and Storage (CCUS) technology will play a pivotal role. Wonder Cement Limited (WCL) is actively collaborating with various technology providers to support this journey. Efforts include segregating greenhouse gas (GHG) emissions from stacks, implementing oxy-fuel technology, electrifying kilns, utilising 100 per cent solar energy within plants, and eliminating fossil fuel consumption.
WCL has conducted a comprehensive GHG inventory aligned with India’s COP26 commitments, aiming to achieve net-zero emissions. Technological innovations such as the installation of a 45 MW Waste Heat Recovery System (WHRS) and an additional 15 MW WHRB have been key milestones. These systems capture excess heat from production processes, converting it into energy and reducing carbon footprints. The company has also introduced advanced burner technology to lower NOx emissions and optimise energy consumption. Currently, WCL achieves less than 47 KWh/tonne of clinker and an SEC of less than 685 Kcal/kg of clinker—benchmarks among the best in the cement industry. These achievements reflect the company’s dedication to lowering environmental footprints through technological enhancements.
What challenges do you face in implementing CCUS in the cement manufacturing process, and how do you address them sustainably?
For India, CCUS is still an emerging concept. While some European companies have successfully implemented CCUS, the associated costs in the Indian context are currently prohibitive, approximately 2.5 to 3 times the cost of a cement plant. This makes large-scale implementation challenging. Some of the key challenges are:
- High project costs: The cost of implementing CCUS is 2-3 times higher than the cost of a cement plant.
- Energy-intensive operations: Operating CCUS facilities can double energy consumption, increasing operational expenses.
- Space requirements: CCUS infrastructure demands substantial space.
- Storage accessibility: Many Indian plants are located inland, far from oceans, complicating carbon storage options.
WCL is advocating for further research to optimise the utilisation of captured carbon, which could lower project and operational costs over time. The company is committed to exploring CCUS feasibility for its future projects and collaborating with technology providers to address these challenges sustainably.
How do you see CCUS contributing to achieving net-zero emissions?
CCUS is indispensable for achieving Net Zero emissions in the cement industry. Even with 100 per cent electrification of kilns and renewable energy utilisation, CO2 emissions from limestone calcination—a key raw material—remain unavoidable. The cement industry is a major contributor to GHG emissions, making CCUS critical for sustainability.
Integrating CCUS into plant operations ensures significant reductions in carbon emissions, supporting the industry’s Net Zero goals. This transformative technology will also play a vital role in combating climate change and aligning with global sustainability standards.
Any specific investments or partnerships made in CCUS research or deployment to support sustainable practices?
WCL has implemented several innovative technologies and process optimisations to minimise GHG emissions. Key initiatives include:
- Installation of WHRS and maximising renewable energy usage.
- Exploring the production of lower clinker cements such as LC3 and PLC, alongside increasing the share of blended cement like PPC.
- Engaging with consultants and technology providers to develop a comprehensive Net Zero and ESG roadmap.
Any success stories or pilot projects involving CCUS that have significantly impacted your sustainability goals?
We have invested in renewable energy projects to significantly reduce its carbon footprint. Key examples include:
- Solar power installations at Nimbahera Integrated Plant and Jhajjar Grinding Unit.
- 15 MW windmills at Pratapgarh.
- Renewable Power Purchase Agreements for grinding units in Aligarh, Uttar Pradesh, and Dhule, Maharashtra, replacing 50 to 60 per cent of energy demand from the grid and reducing GHG emissions.
The company is actively exploring CCUS installation for upcoming projects, assessing its viability in the Indian context.
Beyond CCUS, what other sustainable practices or innovations is your company implementing to reduce its environmental footprint?
WCL’s sustainability initiatives include:
Energy efficiency: Installing Variable Frequency Drives (VFDs), optimising differential pressures across bag filters, and enhancing kiln operations.
- 3R principles: Emphasising reduce, reuse and recycle to optimise resource utilisation and waste management.
Waste co-processing: Utilising over 50,000 tonnes of RDF/plastic waste and ensuring proper disposal of hazardous waste like used oil and lead-acid batteries. - Alternative raw materials: Substituting natural resources with industrial by-products like red mud, chemical gypsum and ETP sludge.
- Plastic waste management: Increasing recycled content in PP bags and achieving Extended Producer Responsibility (EPR) targets.
- Carbon sequestration: Planting over 250,000 trees, sequestering 5,000-10,000 tonnes of CO2 annually.
- Water conservation: Operating as a water-positive organisation, with a focus on rainwater harvesting and groundwater recharge.
How do you balance the cost challenges of CCUS with your commitment to sustainable development?
WCL prioritises environmental stewardship alongside financial sustainability. While CCUS implementation involves high costs, WCL sees opportunities in mechanisms such as Carbon Border Adjustment Mechanism (CBAM), carbon trading, and Renewable Energy Certificate (REC) trading. These avenues provide financial incentives to offset the initial investment in green technologies.

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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