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CHAPTER 7

Refuse-Derived Fuel and Cement Co-Processing

RDF & Cement Co-processing

Pre-processing of dry waste fraction (paper, plastic, textile, leather, wood) into Refuse-Derived Fuel (RDF) — pellets, fluff, briquettes — for use in cement kilns, dedicated waste-to-energy plants, or industrial boilers. RDF specification, calorific value, contamination limits, integration with MRF, financial viability, role in waste diversion from landfill.

RDF & Waste-to-EnergyManual on Municipal Solid Waste ManagementRevised Edition (2016) with SBM 2.0 (2021) + Plastic Waste / E-waste Rules updates

Key formulas

  • RDF calorific value (LCV) MJ/kg = 4.18 × HHV (kcal/kg) − latent heat of moisture; typical 12-18 MJ/kg
  • RDF yield = (paper + plastic + textile + leather fraction) × (1 − impurity removal); typical 15-25% of input MSW
  • RDF substitution ratio (cement kiln): 1 tonne RDF (15 MJ/kg) ≈ 0.6 tonne coal (25 MJ/kg) thermally
  • Energy recovery (kWh/tonne MSW for WTE) = LCV × steam-cycle-efficiency × electrical-conversion; ~400-700 kWh per tonne MSW

Key values & thresholds

rdf LCV MJ per kg
12 - 18 (Indian typical)
rdf LCV MJ per kg high grade
18 - 22 (for substitute fuel grade)
rdf moisture max pct
20 (preferred) - 30 (acceptable)
rdf chlorine max pct
0.7 - 1.0 (for cement kiln)
rdf sulphur max pct
1.0
rdf ash max pct
15 - 20
rdf size pellet mm
10 - 50
rdf size fluff mm
< 100
rdf yield from MSW pct
15 - 25 (depends on dry waste fraction + segregation)
rdf capex INR crore per 50TPD processing
10 - 25
rdf substitution in cement target pct
30 (typical Indian cement plant by 2030)
rdf market price cement INR per tonne
1500 - 3500 (delivered to cement plant)
co processing tipping fee INR per tonne
500 - 2000 (paid by ULB to cement plant)
wte dedicated plant capex INR crore per MW
15 - 25

Clause-level requirements

  • RDF facility shall accept source-segregated dry waste; mixed waste shall be pre-processed via MRF (chapter 4) for contamination removal.
  • RDF specification shall meet end-user requirement: cement kiln (LCV ≥ 14 MJ/kg, Cl ≤ 0.7-1.0 %, moisture ≤ 20 %) OR dedicated WTE (more flexible).
  • Pre-processing shall include: shredding, magnetic + eddy-current separation, drying, size sorting, density separation, pelletisation/baling.
  • Cement co-processing shall be approved by SPCB + comply with emission norms (CPCB common emission standards for waste co-processing).
  • RDF storage shall be sealed/covered to prevent moisture re-absorption + dust + fire risk.
  • RDF shall not be used for combustion in non-emission-controlled boilers (small industries, brick kilns) — air quality concern.

Practitioner notes — what goes wrong in the field

  • RDF is the dry-waste counterpart to composting/biomethanation — handles paper, plastic, textile, wood fractions that composting can't.
  • Indian cement industry consumes ~10-15 % of waste-derived fuel (TSR — Thermal Substitution Rate); target is 30 % by 2030. Major demand-side pull for RDF.
  • Cement kilns are excellent for RDF: 1450-2000°C combustion temperature destroys all organics + dioxins; 4-7 second residence time; alkaline environment neutralises HCl + SO2; ash becomes part of clinker.
  • Co-processing economics: ULBs PAY cement plants ₹500-2000/tonne tipping fee for taking RDF; RDF replaces coal (₹4500-7000/tonne) saving cement plants ₹1500-3500/tonne. Win-win.
  • Top Indian cement co-processors: UltraTech, ACC, Ambuja, Shree, Dalmia, JK — most have multiple plants accepting RDF from cities within ~200 km radius.
  • RDF specification matters: cement kilns are picky. LCV ≥ 14 MJ/kg, chlorine ≤ 0.7-1.0 % (chloride embrittles equipment), moisture ≤ 20 %, ash ≤ 15-20 %. Not meeting spec = rejection.
  • Pre-processing infrastructure: shredder → magnetic separator → eddy-current separator (non-ferrous) → drying (often passive sun-drying in India) → density separator → pelletiser/baler. Capex ₹10-25 cr per 50 TPD.
  • RDF for dedicated WTE plants (chapter 8): more lenient spec (chlorine, moisture more tolerant); but WTE economics in India are challenging.
  • WARNING: RDF must NOT be combusted in uncontrolled boilers (small industries, brick kilns). Without flue gas scrubbing, dioxin + heavy metal emissions are dangerous. CPCB norms apply only to controlled installations.
  • RDF storage: covered + sealed to prevent moisture re-absorption (degrades calorific value) + dust + spontaneous combustion risk (especially in monsoon).
  • Cost (2026): RDF processing facility ₹10-25 cr per 50 TPD throughput; produces 10-15 TPD RDF (15-25 % yield); RDF sells at ₹1500-3500/tonne to cement; tipping fee ₹500-2000/tonne (ULB pays to cement plant).

FAQs

What's RDF (Refuse-Derived Fuel)?
Pre-processed combustible fraction of MSW — paper, plastic, textile, leather, wood — turned into pellets, fluff, or briquettes for combustion in cement kilns or dedicated waste-to-energy plants. Calorific value 12-18 MJ/kg (vs 4-8 for raw MSW; 18-25 for coal). Typical yield: 15-25% of input MSW.
Why send RDF to cement kilns?
Cement kilns are excellent destruction environment: **1450-2000°C** combustion + 4-7 second residence + alkaline atmosphere neutralises HCl/SO2 + ash becomes clinker. Cement industry target: **30% Thermal Substitution Rate by 2030**. ULBs save landfill space + revenue from tipping fee; cement plants save coal cost. Win-win.
What's the RDF specification for cement kilns?
LCV ≥ 14 MJ/kg, chlorine ≤ 0.7-1.0% (chloride embrittles equipment), moisture ≤ 20%, ash ≤ 15-20%, sulphur ≤ 1.0%. Per IS 17219:2019 + CPCB Common Emission Standards for Waste Co-processing 2017. Pellets 10-50 mm OR fluff < 100 mm.
How much does an RDF facility cost?
₹10-25 crore per 50 TPD throughput (shredder + separators + drier + pelletiser). Yields 10-15 TPD RDF at 15-25% conversion. RDF sells to cement plants at ₹1500-3500/tonne; ULB pays cement plant tipping fee of ₹500-2000/tonne. Net cost depends on city + cement plant location.
Can I use RDF in any boiler?
**No** — only in CPCB-approved emission-controlled installations (cement kilns, dedicated WTE plants with flue gas scrubbing). Combustion in uncontrolled boilers (small industry, brick kilns) creates dangerous dioxin + heavy metal emissions. Strictly prohibited per CPCB + MoEFCC.

Cross-references

MSW Rules 2016 (processing)CPCB Common Emission Standards for Waste Co-processing in Cement Kilns (2017)Cement Manufacturers Association AFR (Alternative Fuel & Raw materials) targetsBEE PAT scheme (cement industry energy efficiency — RDF qualifies)IS 17219:2019 (Refuse Derived Fuel — specification)MoEFCC notifications on co-processing

Tags

refuse derived fuelRDFcement co-processingalternative fuelAFRcalorific valuepelletisationwaste diversionco-processing

Engineer's notes

Refuse-Derived Fuel (RDF) is the dry-waste counterpart to composting + biomethanation. While those handle the biodegradable fraction, RDF processes the combustible dry fraction — paper, plastic, textile, leather, wood — that doesn't compost.

The process: source-segregated dry waste enters pre-processing (shredder → magnetic separator removes ferrous → eddy-current separator removes non-ferrous → drying → density separator removes inerts → pelletiser/baler creates uniform fuel). Output: 10-50 mm pellets (or fluff < 100 mm) with calorific value 12-18 MJ/kg, suitable for substitution of coal in cement kilns or dedicated WTE plants.

Why cement kilns: they're the ideal destruction environment. 1450-2000 °C combustion temperature destroys all organics + dioxins; 4-7 second residence time ensures complete combustion; alkaline atmosphere neutralises HCl + SO2 emissions; ash becomes part of clinker (no separate ash disposal). The Indian cement industry uses ~10-15 % alternative fuel currently, with a 30 % Thermal Substitution Rate target by 2030 — massive demand-side pull.

The economics work: ULBs pay cement plants ₹500-2000/tonne tipping fee (vs ₹500-1500/tonne landfill cost). Cement plants save ₹1500-3500/tonne by displacing coal (which costs ₹4500-7000/tonne, with calorific value 25 MJ/kg vs 15 for RDF). Net win for both parties.

Top Indian co-processors: UltraTech, ACC, Ambuja, Shree Cement, Dalmia, JK Cement — most have multiple plants accepting RDF from cities within ~200 km radius. Project economics depend on this transport distance.

Specification matters: cement kilns are picky. Chlorine ≤ 0.7-1.0 % (chloride embrittles kiln equipment + corrodes preheaters), moisture ≤ 20 % (degrades calorific value + adds heat-up energy), ash ≤ 15-20 %, LCV ≥ 14 MJ/kg. RDF not meeting spec gets rejected — wasted production cost.

Pre-processing capex: ₹10-25 crore per 50 TPD throughput. Yields 10-15 TPD RDF at 15-25 % conversion ratio.

Critical warning: RDF must NOT be combusted in uncontrolled boilers (small industries, brick kilns). Without proper flue gas scrubbing, dioxin + heavy metal emissions are dangerous. CPCB norms apply only to approved installations — cement kilns + dedicated WTE plants with emission control. Strictly prohibited otherwise.

Storage: covered + sealed to prevent moisture re-absorption (degrades CV), dust generation, + spontaneous combustion risk (especially in monsoon humidity).

Where this chapter sits: RDF + cement co-processing handle the dry-combustible fraction (~15-25 % of MSW) that wouldn't otherwise be recycled or composted. Combined with composting + biomethanation (50-60 %) + recycling via MRF (15-20 %), this leaves 5-15 % residue for landfill (chapter 9). The RDF route is increasingly the preferred alternative to dedicated WTE plants (chapter 8) due to better economics + lower technology risk.

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Manual on Municipal Solid Waste Management · Revised Edition (2016) with SBM 2.0 (2021) + Plastic Waste / E-waste Rules updates · Central Public Health and Environmental Engineering Organisation (CPHEEO), Ministry of Housing and Urban Affairs, Government of India.
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