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Chapter 17 — Construction and demolition wastes Non-Hazardous

EWC Code

17 08

Gypsum-based construction material

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

Annual Volume

~25 Mt/year EU (CDW gypsum); ~1.5 Mt/year industrial gypsum by-products

Valorisation Range

€10–50/tonne processed recycled gypsum

Primary Route

Wallboard Recycling (Closed Loop)

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Waste Classification

EWC 17 08 covers gypsum-based materials arising from construction and demolition, principally plasterboard (drywall) waste and plaster coatings. The chapter also encompasses industrially-derived gypsum streams classified under C&DW routes when managed at construction sites — including synthetic gypsum from FGD power station scrubbing, and specialised variants such as red gypsum from TiO₂ manufacture and phosphogypsum from fertiliser production.

Red gypsum is a distinctive iron-bearing calcium sulphate by-product arising from the sulphate-process route to titanium dioxide (TiO₂) production. Ilmenite ore reacts with sulphuric acid, generating iron(II) sulphate (copperas, FeSO₄·7H₂O) as a co-product. Neutralisation of the acid waste liquor with limestone or lime precipitates a reddish-brown calcium sulphate dihydrate rich in iron oxides — hence the name "red gypsum". Huntsman Pigments (Teesside, UK) and Kronos (Germany, Belgium) are the principal European producers, generating approximately 400,000–600,000 tonnes per year of red gypsum between them.

Plasterboard CDW requires source-segregated collection to achieve the 85%+ gypsum purity needed for wallboard manufacturing re-entry. Mixed CDW gypsum contaminated with paper, insulation and metal fixings is downgraded to soil amendment, cement retarder or landfill cover material. The EU Construction Products Regulation (CPR) and Circular Economy Action Plan push member states toward mandatory separate collection of CDW gypsum streams by 2027, following Denmark and Germany which already have operational collection networks.

Typical Generators

Plasterboard demolition from commercial and residential strip-outs
TiO₂ production plants (red gypsum by-product)
Phosphoric acid fertiliser plants (phosphogypsum)
Plasterboard manufacturing trim and off-cut waste

Disposal & Valorisation Routes

Established valorisation pathways for EWC 17 08, ranked by economic value and market depth. Wallboard Recycling (Closed Loop) is the primary route.

Wallboard Recycling (Closed Loop)

Primary

Source-segregated plasterboard waste (≥85% CaSO₄·2H₂O purity) is paper-stripped, dried and crushed to recycled gypsum powder for re-entry into new plasterboard manufacture. Knauf, Saint-Gobain and British Gypsum operate on-site or contracted gypsum recycling closed-loop programmes. Premium paid vs. landfill: €25–40/t diverted.

Cement Retarder (Calcium Sulphate)

Secondary

Ground recycled gypsum (<0.5% chloride, <0.3% Cl from paper) used as a cement set-retarder displacing natural gypsum in Portland cement grinding. Meets EN 197-1 additive specification. Red gypsum requires iron content assessment — excess Fe₂O₃ can affect cement colour but does not impair binding performance.

Agricultural Soil Amendment

Secondary

Calcium sulphate improves heavy clay soil structure, supplies sulphur (S) for brassicas and oilseed rape, and ameliorates sodic soils by displacing Na⁺ with Ca²⁺. Red gypsum additionally contributes iron as a micronutrient. Application rates of 1–5 t/ha under EA guidance require nutrient and heavy metal assessment to confirm compliance with Nitrates Directive.

These are the established routes for EWC 17 08. 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 lime and plaster

Recycled gypsum powder as primary raw material substitute in plasterboard and interior plaster manufacturing

02
Manufacture of cement

Ground gypsum as cement set-retarder at clinker grinding stage

03
Support activities for crop production

Agricultural gypsum application for soil structure improvement and sulphur nutrition

04
Treatment and disposal of non-hazardous waste

Mixed or contaminated gypsum failing quality thresholds — specialist gypsum landfill required (H₂S risk mitigation)

Source: NACE Rev.2 — Eurostat, 2008

Regulatory Context

Key legislative frameworks governing EWC 17 08 classification, transport, and treatment.

Gypsum Landfill Segregation Requirement

Gypsum must NOT be co-disposed with biodegradable waste in landfill. When gypsum and biodegradable materials co-decompose anaerobically, H₂S (hydrogen sulphide) is generated — a toxic, flammable gas. EA/Environment Agency guidance requires dedicated gypsum landfill cells or gypsum-inert cell separation.

Red Gypsum By-Product Status

Huntsman and Kronos have pursued Article 5 WFD by-product status for red gypsum in the UK and Germany respectively, enabling direct sale as soil amendment and construction material without waste carrier documentation. Achieving by-product status requires consistent quality specification and a guaranteed pre-arranged market.

Construction Products Regulation

Recycled gypsum entering plasterboard manufacture must meet EN 13279-1 (building plasters) quality criteria. Mandatory CE marking of plasterboard ensures end-product compliance; recycled input material specification is the manufacturer's responsibility and audited under ISO 14001 environmental management.

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Industries That Use This Waste

Sectors that valorise EWC 17 08 as an input material or secondary raw material.

Explore EU waste flows — Waste Atlas

Visualise 17 years of E-PRTR industrial facility data. See how EWC 17 08 and related waste streams flow across European industries and sectors.

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Source: EUR-Lex Commission Decision 2000/532/EC · NACE Rev.2 — Eurostat 2008

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