EWC Code
Wastes from pulp, paper and cardboard production and processing
EUR-Lex Commission Decision 2000/532/EC — Official Journal L 226, 06/09/2000Annual Volume
~35 Mt/year EU (fibre rejects, sludge, ash, dregs and grits)
Valorisation Range
Fibre rejects for board €10–30/t; biosludge biogas €20–40/t avoided; ash for cement €5–15/t
Primary Route
On-site energy recovery (bark boiler / recovery furnace)
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Get contacts for EWC 03 03EWC 03 03 covers the diverse waste and by-product streams from pulp manufacturing and paper/board production: fibre-rich rejects (primary sludge, screen rejects, broke), biological treatment sludge (biosludge), causticising residues (green liquor dregs, lime mud/grits), ash from bark boilers and recovery furnaces, and de-inking sludge from recovered paper processing. The EU pulp and paper sector processes ~90 Mt of fibre annually, making this a significant industrial waste category.
Primary fibre sludge (fine fibres, fines, fillers) is the largest stream by mass in integrated mills. It can be dewatered and used in board production, composted or burned. Biosludge from activated sludge treatment of mill effluent has lower calorific value but is typically co-fired with bark in the mill's power boiler. De-inking sludge from recovered paper mills contains ink particles, fillers and short fibres — its management is a major operational cost, typically composted, landfilled or used as soil amendment. Dregs and grits from lime cycle operations are typically landfilled or used in construction.
Integrated kraft pulp mills are largely energy self-sufficient through recovery furnace combustion of black liquor and bark, but generate causticising waste (dregs, grits) requiring dedicated disposal routes. The IED BAT Reference Document for pulp and paper defines BAT-associated emission levels and waste minimisation techniques. Increasing fibre recovery from de-inking sludge and ash-to-cement routes are active areas of industrial symbiosis development.
Typical Generators
Established valorisation pathways for EWC 03 03, ranked by economic value and market depth. On-site energy recovery (bark boiler / recovery furnace) is the primary route.
Bark, biosludge, primary sludge and rejects dewatered and co-fired in mill power boiler or recovery furnace. Generates steam and power for on-site use. BAT for kraft mills includes maximising internal energy recovery before export of residues.
Fibre rejects to board and packaging manufacturers; primary sludge to composting; ash to cement kilns as raw material substitute; dregs to road construction aggregate. Requires testing and product quality agreements with receivers.
Dregs, grits and de-inking sludge not meeting product quality specifications for reuse disposed at permitted non-hazardous landfill. Leachate from high-pH causticising waste (dregs) may require pre-treatment before landfill acceptance.
These are the established routes for EWC 03 03. Which one your stream qualifies for depends on its composition, volume and region.
Get the ranked options for your streamPrimary & secondary off-takers
Primary generator; fibre rejects recycled into lower-grade paper and board grades
Cement kilns use paper ash as raw material (silica/alumina) and primary sludge as fuel substitute
Composting and biogas facilities process de-inking sludge and biosludge
Dregs and grits used as construction fill or aggregate where chemistry permits
Source: NACE Rev.2 — Eurostat, 2008
Key legislative frameworks governing EWC 03 03 classification, transport, and treatment.
BAT specifies waste minimisation measures including fibre recovery from reject streams, biosludge co-firing, and ash reuse. BAT-AEL for solid waste generation is sector-specific; kraft mills benchmark against dregs/grits per tonne of pulp produced.
Paper fibre rejects meeting by-product criteria (directly usable, certain further use, no further processing needed, no adverse impacts) can exit waste regulation. De-inking sludge rarely meets these criteria due to variable quality.
Dregs and causticising waste with high pH require pre-treatment (neutralisation) before acceptance at non-hazardous landfill under the landfill acceptance criteria (EN 12457). Organic content limits apply to biodegradable fractions.
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Sectors that valorise EWC 03 03 as an input material or secondary raw material.
Waste-stream pages and resources connected to EWC 03 03 valorisation.
Explore EU waste flows — Waste Atlas
Visualise 17 years of E-PRTR industrial facility data. See how EWC 03 03 and related waste streams flow across European industries and sectors.
Source: EUR-Lex Commission Decision 2000/532/EC · NACE Rev.2 — Eurostat 2008
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