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BRSR Core became mandatory for India’s top 150 listed companies by market cap from FY2023-24 and for the top 1,000 from FY2024-25. It requires reasonable assurance on nine Key Performance Indicators including verified Scope 1 and Scope 2 GHG emissions, energy intensity, water intensity, and selected Scope 3 emissions. For industrial companies also under CCTS, the two frameworks produce essentially the same GHG data — but with different verification standards and different penalties for non-compliance. This article maps the overlap, the divergences, and the dual-framework compliance strategy.
Secondary aluminium produced by melting scrap rather than smelting bauxite, has embedded emissions approximately 10 to 15 times lower than Indian coal-based primary aluminium. Under CBAM, this translates to an approximately €900–1,400/t cost advantage on EU exports. India’s secondary aluminium sector is significantly under-invested relative to this economic opportunity — largely because scrap supply chains are fragmented and the true CBAM economics have not been adequately modelled by secondary producers. This analysis maps the full picture.
CBAM does not cover all steel, all aluminium, or all fertilisers. It covers specific goods defined by EU Combined Nomenclature (CN) codes under Annex I of Regulation EU 2023/956. An Indian exporter that misclassifies its products, either including non-covered goods in its CBAM declaration or excluding covered goods faces either unnecessary compliance cost or regulatory violation. This is the practical classification guide that every Indian CBAM compliance officer needs.
India’s Climate Finance Taxonomy released in draft in May 2025 and under consultation defines which economic activities and assets qualify for green and transition finance labelling in India. For CFOs at steel, aluminium, and fertiliser companies, the taxonomy determines access to sovereign green bond proceeds, sustainability-linked lending terms, and eventual alignment with the global sustainable finance architecture. The draft thresholds are more demanding than many industry participants anticipated. This analysis maps exactly which production routes qualify, which are excluded, and what asset-level actions enable taxonomy eligibility.
On April 10, 2026, the European Parliament’s ENVI Committee published a draft report proposing five major changes to CBAM. The most consequential for India: extending CBAM to approximately 180 additional steel and aluminium-intensive downstream products from January 1, 2028. Auto components, machinery parts, fabricated metal products, tubes, pipes, fasteners, and aluminium containers are all in the proposed scope. One third of India’s downstream steel exports are produced by MSMEs that lack the emissions monitoring infrastructure that CBAM compliance requires. The pre-consumer scrap rule change — which would include emissions from pre-consumer scrap inputs in CBAM calculations — directly threatens the low-carbon advantage that India’s secondary aluminium and scrap-EAF steel sectors currently enjoy. India has less than 21 months to prepare.
The leaked EU CBAM provisional benchmark published in December 2025 contains the single most commercially important number for India’s aluminium industry: the secondary aluminium CBAM benchmark is 0.139 tCO₂e per tonne — versus 1.464 tCO₂e per tonne for primary aluminium. When more than 50% of aluminium is sourced from scrap, the secondary production route applies. India’s secondary aluminium industry, which produces at approximately 0.3-1.3 tCO₂/t depending on the energy source used for remelting, sits well below both the secondary benchmark and the primary benchmark. At EU ETS prices of approximately €60/tCO₂e, this means an Indian secondary aluminium exporter to the EU pays approximately €8/t in CBAM certificates while an Indian primary coal-CPP aluminium producer paying the default rate faces certificates at approximately €800/t. The CBAM gap between primary and secondary aluminium is the largest carbon cost differential in any CBAM-covered product category. This article maps India’s secondary aluminium sector — production volumes, scrap supply dynamics, energy consumption advantage, CCTS targets (finally gazette-notified on January 16, 2026), and the investment case for scaling secondary production as the CBAM advantage crystallises commercially from the first annual declaration in May 2027.
India’s CCTS Detailed Procedure (BEE, July 2024) defines a precise Monitoring, Reporting, and Verification framework that every obligated entity must follow before submitting Form A to the ICM portal by approximately July 31, 2026. The GEI calculation covers Scope 1 direct combustion emissions, Scope 1 direct process emissions, and Scope 2 indirect emissions from purchased electricity and heat — all within a gate-to-gate boundary that the entity fixes at the start of the trajectory period and cannot change without BEE approval. Emission factors are either Type I (IPCC or statutory body published) or Type II (entity-derived through fuel sampling and analysis). A monitoring plan must be documented before data collection begins. ACVA verification is mandatory — no self-certification is permitted. The ACVA cannot have a conflict of interest with the entity it verifies. Verification typically takes 8-12 weeks. BEE’s completeness check takes 10 working days; technical review takes 30-plus days. An entity that begins ACVA engagement in mid-April 2026 is at the outer limit of making the July deadline. This article builds the complete MRV operations guide from the BEE Detailed Procedure: what to measure, how to calculate it, how verification works, what Form A requires, and the five errors that most commonly cause BEE to reject or query a submission.
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India’s primary aluminium smelters run on captive coal power plants that produce 13-19 tCO₂ per tonne of aluminium — 80% of which comes from electricity. Captive solar and wind now cost Rs 4-4.5/kWh all-in, versus Rs 6/kWh for coal CPP. But the cost saving alone understates the investment case. When CCTS Scope 2 GEI reduction, CBAM Scope 2 certificate savings on EU exports, and RCO compliance value are combined with the direct electricity cost saving, a smelter shifting 1 MWh from coal CPP to captive RE earns approximately Rs 6.56/kWh in combined returns — more than the electricity itself costs. A 500 MW captive solar plant generates approximately Rs 574 crore per year in combined returns on a capex of Rs 2,000-2,500 crore — a payback of 3.5 to 4.5 years. This is not an ESG commitment. It is the highest-returning single capital investment available to an Indian aluminium smelter in 2026. This article builds the unified investment model, maps where each rupee of return comes from, and explains the timing logic that makes 2026-2027 the window that matters.
India’s Department of Economic Affairs published the draft Climate Finance Taxonomy in May 2025 — covering power, mobility, buildings, agriculture, and for the first time, hard-to-abate sectors including iron, steel, aluminium, and cement as transition activities. The taxonomy creates a two-tier structure: Tier 1 for directly green activities (renewable energy, clean transport) and Tier 2 for activities that reduce emissions intensity in sectors where zero-carbon alternatives are not yet commercially viable. For industrial companies, taxonomy alignment unlocks access to green bonds, transition bonds, and sustainability-linked loans at financing cost savings of approximately 20 to 80 basis points versus conventional debt. On a Rs 500 crore project, 50 basis points of greenium over a 12-year project life equals approximately Rs 30 crore in cumulative interest saving. The taxonomy’s Technical Screening Criteria — which have not yet been finalised in sectoral annexures — will determine whether specific investments in EAF steelmaking, aluminium smelter RE transition, green ammonia, and waste heat recovery qualify for green or transition finance labelling. This article maps what is already clear, what remains open, and what industrial CFOs should be doing right now to position their CCTS-verified GEI data as taxonomy eligibility evidence.
