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Chapter 10 — Wastes from thermal processesSub-code of EWC 10 11 Non-Hazardous

EWC Code

10 11 10

Waste preparation mixture before thermal processing, other than those in 10 11 09

EUR-Lex Commission Decision 2000/532/EC — Official Journal L 226, 06/09/2000

Annual Volume (EU)

4.8 million tonnes/year EU glass production waste

Valorisation Range

€220M cullet and glass waste market

Primary Route

Glass furnace cullet remelting

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EWC 10 11 10 is a specific sub-code under EWC 10 11 — Wastes from manufacture of glass and glass products. The classification guidance below applies to this waste stream.

Glass manufacturing generates waste glass (cullet), refractory waste, batch dust and off-gas treatment residues as primary waste streams. In-house cullet from glass furnace operations is remelted directly as the highest-priority recovery route, typically comprising 20–30% of furnace batch in primary production. Every 10% increase in cullet use reduces furnace energy consumption by approximately 2.5% and CO₂ emissions proportionally.

Refractory waste from glass tank furnace rebuilds arises every 5–12 years per furnace. Silica and alumina refractories from the melting zone contain residual glass and chromium oxide from checker brickwork, potentially requiring hazardous waste classification. Furnace dust collected in bag filters contains fine glass, batch carryover and volatilised lead, arsenic and barium from specialty glass formulations.

Specialty glass production (optical, borosilicate, lead crystal, CRT) generates waste streams with specific regulatory requirements. Lead crystal cullet containing >24% PbO requires management as hazardous waste. CRT glass contains lead in the panel and cone glass (up to 25% PbO in cone) and barium in panel glass; processing requires licensed e-waste facility. Commission Regulation 1179/2012 establishes end-of-waste criteria for cullet (excluding CRT and lead glass).

Typical Generators

Flat glass manufacturers
Container glass producers
Special glass manufacturers
Glass wool and fibre producers
CRT and display glass recyclers

Disposal & Valorisation Routes

Established valorisation pathways for EWC 10 11 10, ranked by economic value and market depth.

Glass furnace cullet remelting

Primary

Clean cullet from production defects is returned to furnace batch as direct energy-saving raw material substitution. Colour-sorted container glass cullet from MRF sorting is sold to container glass furnaces. Flat glass cullet returned to float glass furnace if within composition specifications.

Alternative glass use and aggregate

Secondary

Mixed or contaminated cullet not suitable for furnace remelting is used as road sub-base aggregate (glasphalt), filtration media for water treatment, sandblasting media and drainage aggregate. Ground glass powder is used as pozzolanic cement replacement or filler in plastics and rubber.

Hazardous processing for lead glass

Backstop

Lead glass (CRT cone, lead crystal) is processed by specialist licensed operators using hydrometallurgical lead recovery or direct remelt for lead alloy production. Refractory containing chromium(VI) from checker brickwork is disposed to hazardous landfill after testing.

These are the established routes for EWC 10 11 10. Which one your stream qualifies for depends on its composition, volume and region.

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NACE Receiving Industries

Primary & secondary off-takers

01
Manufacture of flat glass

Remelt clean float glass cullet in furnace batch to reduce energy and raw material costs

02
Manufacture of hollow glass

Use colour-sorted container glass cullet as principal furnace batch component

03
Manufacture of ready-mixed concrete

Use crushed glass as supplementary cementitious material or fine aggregate in concrete

04
Dismantling of wrecks

Process CRT and lead crystal glass waste for lead recovery at licensed WEEE facility

Industries That Use This Waste

Sectors that valorise EWC 10 11 10 as an input material or secondary raw material.

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