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Role of Waste-to-energy, WtE, in the circular economy, CE
Prof. Em. Carlo Vandecasteele University of Leuven, Belgium
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Waste hierarchy In this conference: not only WtE discussed, but also other methods of waste treatment Waste hierarchy gives degree of priority of these Material recycling Composting Why not prevent, recycle, reuse, all waste? WTE Combustion without E recovery Landfill
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Circular Economy Does WtE still have role to play in CE?
In Europe more and more the concept of Circular Economy is promoted → Sustainable Development CE is defined as economy that ‘maintains value of products, materials & resources for as long as possible in circulation in economy, minimising waste and resource use’ Prevention, preparing for reuse, recycling, all 3 perfectly fit in CE Not obvious for WtE WtE believed to compete with recycling (higher in Hierarchy) Does WtE still have role to play in CE?
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Does WtE still have role to play in CE?
EC (2017): (prudent) WtE can play role in transition to CE, provided waste hierarchy used as guiding principle, higher levels (prevention, reuse, recycling) not prevented My answer: unambiguous yes, and I mean that WtE has an essential role to play, for 6 reasons
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1. WtE combusts (should combust) only waste that to date cannot be recycled, for
Technical reasons Insufficient separate collection; sorting, purification impossible No methods to produce recycled material, at reasonable cost Some waste (plastic/paper/textile) only recycled limited no. of times, because fibres shorten Economic Low market value for recycled product, material High Capex, Opex for separate collection, sorting, purification Energy consumption > production from virgin materials Recycling cost > production from virgin materials Environment, safety and health Recycling may dissipate toxic substances over recycled products, source of human exposure, e.g. PBDEs from WEEE plastics
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1.WtE combusts (should combust) only waste that to date cannot be recycled
In many countries fractions of household waste collected selectively →recycling/composting: vegetables-fruit-garden waste; paper and cardboard, metals, construction and demolition waste, hazardous waste, etc. In Flanders (North of Belgium) 70.4 % (2014) collected selectively Residual waste, i.e. waste currently not recycled, along with recycling residue (to date 33%), goes to WtE, because of landfill ban for MSW In future, it is expected residual waste will decrease ← increased prevention, increased selective collection recycling will increase ← design for recycling, avoiding toxic compounds, better recycling technology …
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2. WtE does not compete with recycling, but with landfill (lower in hierarchy)
EU more recycling+ composting thanWTE, more WtE than landfill. GE, SW B DK AU, CH, NO < 3% landfill, landfill ban, MA, RO less advanced waste management, mainly rely on landfill. Countries with lot of recycling also lot of WTE, WtE and recycling complementary: No competition WtE ↔ recycling (higher in hierarchy), WtE ↔ landfill (lower in hierarchy)
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3. WtE is essential to keep hazardous materials out of CE
For waste containing toxic substances, WtE preferred over recycling, ex. PBDEs from WEEE plastics Combustion (WtE) destroys toxic organic substances recycling spreads it. High conc’n → high T techniques, e.g. rotary kiln with secondary combustion WtE retains HM in solid residues (FGC residues): S/S, stored in landfill → WtE keeps materials, environment free of toxic substances
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4. Allows material recycling from non-recyclable waste
Combustion of MSW: kg of bottom ash/ton of MSW Heterogeneous: ash, stones, metals Broad particle size distribution, 1-25 mm 4. Allows material recycling from non-recyclable waste
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4. Allows material recycling from non-recyclable waste
From BA can be recycled: Metals: most valuable (recently interest for precious metals) Mineral fraction: largest mass, volume For recycling, e.g. as construction material, BA should comply with concentration and/or leaching limits. Often exceeded for e.g. Cu, Mo, Sb, Cl-,SO42- In general treatment required before recycling
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4. Allows material recycling from non-recyclable waste.
State-of-the-art BA separation of 10 years ago: Integrated Municipal Solid Waste Treatment Using a Grate Furnace Incinerator: The Indaver Case C Vandecasteele et al. Waste Manag 27, 1366, 2006 More recently considerable progress in BA treatment: separation, sorting of metals, of mineral fractions Wet, half dry (moist), dry treatment Pneumatic sensor based sorting Special treatments for reducing leaching of Cu, Sb Recycling of MSWI Bottom Ash: A Review of Chemical Barriers, Engineering Applications and Treatment Technologies, B. Verbinnen, C. Vandecasteele et al., Waste biomass valor, 8, 1453, 2017 Ferrous (8.5%) and NF(1%) recycled. Purity often better than when directly separated from MSW (e.g. food can). Metal oxidation rather limited. Sand and Granulates (< 2mm, 2-6 mm, 6-50 mm) aged, carbonated to reduce metal leaching
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4. Allows material recycling from non-recyclable waste.
Bulk application Artificial hills, e.g. ‘Green ship’ Subbase in road construction Embankment, noise barrier Raw material in cement production Production of ceramics Landfill cover Structured construction material BA fractions mixed in concrete as (Partial) sand replacement, (Partial) gravel replacement (Partial) cement replacement after activation
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5. May generate energy with high efficiency
In WtE, HP, HT steam generated in boiler, applied in a Rankine (superheated) steam cycle to generate electricity using turbine, as in fossil fuel power plant In WtE less advanced steam conditions (400°C, 40 bar) ← flue gas (more Cl, Na, K) corrosive, and smaller installations → lower ηe (typically 20-25%) Using other boiler materials to avoid HT corrosion → advanced steam cycle possible e.g. AEB, Amsterdam: complicated, very expensive ηe = η = 31%
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5. May generate energy with high efficiency
Low η occurs when only electricity generated, residual energy, heat lost Other possibilities: generate electricity, and also use residual thermal energy (LP, LT steam, hot water) for heating greenhouses, hospitals, offices, district heating, … CHP → higher overall η use HT, HP steam (partly) directly→ higher overall η (up to 80-90%)
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5. May generate energy with high efficiency CHP
Gotenburg, Stockholm, Kopenhagen, Vienna, Paris… large district heating networks fed by WtE incinerators in, near the city Additional advantage: short MSW transport
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Location: Antwerp port– Waasland port
5. May generate energy with high efficiency Exampe of direct use of steam ECLUSE industrial steam network, in Antwerp port Condensate return duct 5 Nearby Chemical companies, large-scale companies need steam for production processes Steam duct (above/ below) ground 5 km Superheated steam 400 °C; 40 bar WtE plant + Waste & sludge Location: Antwerp port– Waasland port In many countries WtE not in or near City, but in industrial area, park
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5. May generate energy with high efficiency
In Antwerp (left bank) Indaver & SLECO operate 3 grate furnace incinerators (household & commercial waste) and 3 fluidized bed incinerators (sludge & industrial waste) Waste throughput: 1,000,000 ton/y; Heat production power: 250 MWth Energy 50% renewable, 50% of CO2 climate neutral Port of Antwerp is home to the largest chemical cluster in Europe Chemical industry: energy intensive, consumption very stable Steam used for: distillation, evaporation/drying, driving endothermic chemical reactions 17
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6. CE needs energy, WtE may partly feed it!
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Conclusion I have shown that WtE
Combusts (should combust) only waste that to date cannot be recycled Does not compete with recycling, but with landfill (lower in WH) Is essential to keep hazardous materials out of CE Allows material recycling from non-recyclable waste May generate energy (50% renewable, climate neutral) with high efficiency CE needs energy, WtE may partly feed it Therefore WtE still has an essential role to play in CE
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