Embracing Circularity — Waste Generated + Recycled Intensity — BRSR Core Attribute
BRSR Core circularity attribute: waste generated by category (plastic, e-waste, hazardous, biomedical, etc.), recycled/reused/disposed split, recycled-input %.
What this attribute is
Embracing Circularity is one of the nine BRSR Core attributes that SEBI requires every Top-1,000 listed entity to subject to independent reasonable assurance under SAE 3000 (Revised). It sits within NGRBC Principle 6 — Environment and is the only BRSR Core attribute whose primary metric is a ratio of material flows (recycled + reused vs disposed) rather than an intensity per rupee.
The attribute captures three numbers:
- Total waste generated in metric tonnes, split by category (plastic, e-waste, biomedical, hazardous, etc.)
- Waste recycled + reused vs disposed split (% of total)
- Recycled input % — share of input materials sourced from recycled / reclaimed sources
ESG-rating screens + circular-economy benchmarks both anchor on the recycled / reused % — a higher number signals more closed-loop material flow and lower landfill / incineration dependence.
What’s in scope — the waste categories
Per the BRSR format Principle 6 Essential Indicator 6, waste is reported separately for each of the following categories:
| Category | Governing Indian rules | Typical sources |
|---|---|---|
| Plastic waste | Plastic Waste Management Rules 2016 (amended through 2024) | Packaging, process-waste plastic, MLP, flexible plastic |
| E-waste | E-Waste Management Rules 2022 | End-of-life computers, monitors, servers, mobile phones, lab instruments |
| Bio-medical waste | Bio-Medical Waste Management Rules 2016 | Hospital / clinic / lab waste; relevant for pharma + healthcare entities |
| Construction + demolition (C&D) waste | C&D Waste Management Rules 2016 | Site demolition + new-build excavation; large quantities for real estate + infrastructure |
| Battery waste | Battery Waste Management Rules 2022 | Lead-acid, Li-ion, Ni-Cd; UPS batteries, vehicle batteries, EV batteries |
| Radioactive waste | Atomic Energy (Safe Disposal of Radioactive Wastes) Rules 1987 | Nuclear / atomic-energy entities only |
| Other hazardous waste | Hazardous + Other Wastes Rules 2016 — Schedule I categories | Spent oil, acid + alkali solutions, paint sludge, incinerator ash, contaminated containers |
| Other non-hazardous waste | (no specific rule; municipal solid waste rules apply) | Canteen waste, office paper, general scrap |
Each category is reported separately in metric tonnes (tonnes; some entities use kg for very small quantities), then aggregated.
The recycled / reused / disposed split
For each waste category, three flows are reported:
- Recycled — waste sent to an authorised recycler for material recovery. The recycler must be CPCB / SPCB authorised for that waste category. Evidence: recycler authorisation certificate + weighbridge slips + EPR credit certificates (for plastic / e-waste / battery).
- Reused — waste returned to the production process or to a different downstream use without material conversion. E.g., process water reused after treatment, packaging returned to vendor, scrap metal returned to the casting furnace.
- Disposed — waste sent to landfill, incineration without energy recovery, deep-well injection, or other terminal disposal. For hazardous waste, disposal must be at a CPCB / SPCB authorised TSDF (Treatment, Storage + Disposal Facility).
The headline circularity metric is:
Recycled + Reused % = (Recycled tonnes + Reused tonnes)
÷ Total waste generated tonnes
A higher % signals stronger circularity. Year-on-year movement is the key ESG-rating signal.
Recycled input percentage
The companion upstream metric:
Recycled Input % = Mass of input materials from recycled / reclaimed sources
÷ Total mass of input materials
For a downstream manufacturer using recycled aluminium scrap as feedstock, recycled plastic flake for packaging, or reclaimed steel for structural components — the recycled-input % captures the upstream circular sourcing. The denominator is total mass of input materials (raw materials + process consumables) per the production records; the numerator is the recycled / reclaimed portion documented from supplier certifications.
This metric is disclosed under Principle 6 Essential Indicator 5 (alongside total input material details) and is part of the BRSR Core assurance scope.
Worked example
Mid-size FMCG entity for FY 2025-26.
Waste output
| Category | Generated (t) | Recycled (t) | Reused (t) | Disposed (t) |
|---|---|---|---|---|
| Plastic waste | 420 | 380 | 0 | 40 |
| E-waste | 8 | 8 | 0 | 0 |
| Battery waste | 2 | 2 | 0 | 0 |
| Other hazardous waste | 120 | 30 | 0 | 90 |
| Other non-hazardous waste | 350 | 60 | 220 | 70 |
| Total | 900 | 480 | 220 | 200 |
Recycled + reused % = (480 + 220) / 900 = 77.8%
Recycled input
| Input material | Total mass (t) | Recycled portion (t) |
|---|---|---|
| Aluminium sheet | 1,200 | 600 (recycled-content aluminium) |
| HDPE packaging | 480 | 240 (recycled-content HDPE) |
| Paper packaging | 150 | 90 (recycled-content kraft) |
| Steel components | 350 | 0 (virgin only) |
| Total | 2,180 | 930 |
Recycled input % = 930 / 2,180 = 42.7%
For year-on-year comparison: FY 2024-25 recycled+reused output % was 71.2% (up 6.6 pp YoY) and recycled input was 35.4% (up 7.3 pp YoY). Both improvements track the entity’s circularity commitments under the Plastic Waste EPR programme + the aluminium recycled-content procurement policy.
Evidence the assurance partner checks
| Document | What it evidences | Issued by |
|---|---|---|
| Form 10 manifest | Hazardous waste transfer to recycler / TSDF | SPCB-issued; carried with each transport |
| Form 4 annual return | Aggregate hazardous waste generated + disposed for the FY | SPCB-issued; entity files annually |
| Plastic Waste EPR certificate trail | EPR credit retirement against plastic introduction quantity | CPCB EPR portal |
| E-Waste EPR certificate trail | EPR credit retirement against EEE introduction quantity | CPCB EPR portal |
| Battery EPR certificate trail | EPR credit retirement against battery introduction quantity | CPCB EPR portal |
| Recycler authorisation certificate | The recycler is authorised for the specific waste category | SPCB / CPCB (per category) |
| Weighbridge slips | Quantity-level evidence of each transfer | Entity’s weighbridge + recycler’s weighbridge |
| Supplier recycled-content declarations | Recycled input % numerator | Supplier-issued |
| Internal waste register / EHS database | Internal aggregation of all waste flows | Entity’s EHS system |
Common audit findings
- Unauthorised recycler chain. Plastic waste routed through an unregistered aggregator before reaching the authorised recycler — breaks the EPR credit chain + creates ESG-rating risk. The recipient at the first transfer point must be CPCB / SPCB-authorised for that category.
- EPR credit double-counting. Same plastic waste tonnage counted as “recycled” by both the brand owner + the recycler; under EPR, the credit certificate is assigned to one party (typically the producer / brand owner) and that’s the only count valid for the BRSR recycled flow.
- Hazardous waste — Form 10 manifest gaps. Transfer to authorised TSDF without Form 10, or with mismatched quantities between Form 10 + weighbridge slip. The variance must be reconciled + documented.
- Recycled vs reused confusion. Process water reused after treatment is recorded as “recycled” instead of “reused” (or vice versa). The distinction matters because the recycled bucket implies material recovery (a downstream recycler converts the waste into a new product), while reused implies same-use without conversion.
- Non-hazardous waste under-captured. Office paper + canteen waste + general scrap is often estimated rather than measured. Best practice: monthly weighbridge entries or contracted municipal pick-up records.
- Battery waste not categorised. UPS batteries replaced under AMC, EV / forklift batteries replaced + handed to vendor under buy-back — these get missed from the battery-waste line. Battery waste has its own EPR framework under Battery Waste Management Rules 2022.
- C&D waste under-recognised. New-plant construction or major shutdown demolition generates large quantities of C&D waste that the EHS team doesn’t always capture (the project team manages it). Need integration between project waste tracking + EHS database.
- Recycled input — supplier declaration not retained. Recycled-content claim from supplier (e.g., “75% recycled HDPE”) needs a written supplier declaration retained as workpaper evidence. Verbal / email confirmation is insufficient for reasonable assurance.
EPR (Extended Producer Responsibility) intersection
For plastic packaging + e-waste + batteries, the EPR framework imposes a parallel obligation: the producer / importer / brand owner (PIBO) must collect + recycle / dispose of waste equivalent to its annual introduction quantity into the market. EPR fulfilment is tracked via the CPCB EPR portals (separate portals for plastic, e-waste, battery).
For BRSR purposes:
- The waste-output figure captures internal waste generated by the entity’s operations
- The EPR credit retirement captures end-of-life waste of products the entity introduced into the market
These are different denominators. An FMCG entity that introduced 1,000 tonnes of plastic packaging may have generated 50 tonnes of plastic waste internally (process scrap) and retired EPR credits equivalent to 1,000 tonnes (covering end-of-life packaging). Both flows are reported, but in different parts of BRSR — the 50 tonnes goes into the Principle 6 EI 6 waste table; the EPR credit retirement is part of the producer responsibility narrative under Principle 2 (Sustainable Products).
For the upstream Principle 2 framework, see NGRBC Principle 2 — Sustainable Products.
XBRL filing
This attribute is filed in the BRSR XBRL instance document under the Principle 6 Essential Indicator 5 (recycled input) + Essential Indicator 6 (waste output) elements from the MCA-published BRSR taxonomy module. Per-category waste quantities + recycled / reused / disposed breakdown + recycled input % are filed as separate elements. Verify element names + unit references against the current MCA taxonomy version before generating the instance document.
Both current-year and previous-year context references must be populated with matching boundary disclosure. See XBRL Taxonomy for BRSR for the structural overview.
How this attribute rolls up into the BRSR Core engagement
This attribute is one of the four Core attributes under Principle 6 (alongside GHG, water, and energy). The signed BRSR Core assurance report attests these numbers to reasonable assurance under SAE 3000 (Revised). Workpapers retained by the assurance partner cover the per-category waste reconciliation, Form 10 manifest sampling, EPR credit certificate trails, recycler authorisation verification, and boundary alignment with the parent entity scope.
For the engagement that produces the signed assurance opinion, see BRSR Core Assurance.
Related reading
- NGRBC Principle 6 — Environment — parent pillar
- NGRBC Principle 2 — Sustainable Products — EPR + product life-cycle linkage
- GHG Emission Intensity per Revenue — sibling Core attribute
- Water Withdrawal Intensity — sibling Core attribute
- Energy Footprint Disclosure — sibling Core attribute
- Document Evidence Requirements — full evidence checklist including waste documents
- XBRL Taxonomy for BRSR — XBRL filing structure
- BRSR Core Assurance — service
Frequently asked questions
What are the BRSR Core waste categories that must be reported?
Per the BRSR format Principle 6 Essential Indicator 6, waste is disclosed by category: plastic waste; e-waste; biomedical waste; construction + demolition (C&D) waste; battery waste; radioactive waste; other hazardous waste (per Schedule I of the Hazardous Waste Rules 2016); other non-hazardous waste. Each category is reported separately in metric tonnes, then aggregated for the total.
What does 'recycled + reused' mean for BRSR Core purposes?
Recycled = waste sent to an authorised recycler for material recovery (input to new product). Reused = waste returned to the production process or to a different downstream use without material conversion (e.g., process water reused after treatment, packaging returned to vendor). Disposed = waste sent to landfill, incineration without energy recovery, deep-well injection, or other terminal disposal. The recycled + reused proportion is the headline BRSR circularity metric.
How is recycled-input percentage calculated?
Recycled input % = (Mass of input materials sourced from recycled / reclaimed sources) ÷ (Total mass of input materials). This is reported alongside waste outputs as part of the circularity narrative. For a manufacturer using recycled aluminium scrap as feedstock, the recycled-input % captures that material substitution upstream.
Is waste intensity per rupee of revenue required?
Per the BRSR Core attribute structure, the primary disclosed metric is the absolute waste in tonnes split by category + the recycled/reused/disposed split. An intensity metric (tonnes per ₹ Crore of PPP-adjusted revenue) is computed for internal management + ESG-rating purposes but is not the primary BRSR Core attribute number. The recycled/reused % is the headline ratio.
What evidence does the assurance partner check for waste figures?
Manifests + Form 10 / Form 4 returns filed with the State Pollution Control Board (SPCB) for hazardous + plastic + e-waste + battery waste; weighbridge slips from the waste recycler / disposer; recycler authorisation certificates (CPCB / SPCB-issued); EPR credit / certificate trails from the centralised EPR portals (CPCB EPR portal for e-waste + plastic + battery). For non-hazardous waste (canteen, office, packaging) — internal weighbridge or pick-up confirmations from the municipal contractor.
How are hazardous wastes handled differently?
Hazardous waste must be tracked by the specific Schedule I waste code under the Hazardous + Other Wastes Rules 2016 (e.g., Cat 4.1 spent oil, Cat 5.1 acidic solutions, Cat 17.3 incinerator ash). Each transfer requires a SPCB-issued Form 10 manifest. The recycler / TSDF (Treatment, Storage + Disposal Facility) must be authorised by the SPCB for that specific waste category. Audit findings on hazardous waste typically involve unauthorised recycler chains or missing Form 10 documentation.
Does plastic waste include all plastic, or only packaging plastic?
BRSR follows the Plastic Waste Management Rules 2016 categorisation: rigid plastic, flexible plastic, multi-layered plastic, compostable plastic. Both packaging plastic + process-waste plastic are included. The EPR framework (extended producer responsibility) requires producers, importers + brand owners to collect + recycle / dispose plastic equivalent to their introduction quantity — EPR credit balance reconciliation is checked during assurance.
What XBRL element is used for this attribute?
Waste data is filed in the BRSR XBRL instance document under the Principle 6 Essential Indicator 6 elements from the MCA-published BRSR taxonomy module. Per-category waste quantities + recycled / reused / disposed breakdown + recycled input % are filed as separate elements. Verify element names + unit references against the current taxonomy version before generating the instance document.