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Chapter 13 — Oil wastes and wastes of liquid fuelsSub-code of EWC 13 04 Hazardous

EWC Code

13 04 01

Bilge oils from inland navigation

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

Annual Volume (EU)

200,000 tonnes/year EU ship-generated bilge waste oil

Valorisation Range

€45M port waste reception facility market

Primary Route

Port waste reception and oil recovery

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EWC 13 04 01 is a specific sub-code under EWC 13 04 — Bilge oils. The classification guidance below applies to this waste stream.

Bilge oils arise from the accumulation of seawater, lubricating oil leakage, fuel leakage and cleaning water in the lowest compartments (bilges) of vessels. EU flag vessels and vessels calling at EU ports are subject to mandatory port state control and MARPOL annex requirements. Bilge water is typically 0.1–2% oil content; bilge oil sludge concentrated by oil-water separator systems is typically 30–70% oil content.

MARPOL Annex I prohibits discharge of bilge water with oil content exceeding 15 ppm from ships outside special areas, and 100 ppm from older ships. Oily bilge water not meeting discharge limits must be retained on board and delivered to port waste reception facilities. Port Reception Facility (PRF) Directive 2019/883/EU requires EU ports to provide adequate reception capacity and report waste delivery quantities.

Bilge oil chemical composition reflects the vessel type and operation: cargo vessels generate mineral oil-dominant bilge; fishing vessels generate fish oil-contaminated bilge requiring separate management. Inland waterway bilge is classified separately (13 04 03) from coastal and ocean-going vessel bilge. Composition determines whether bilge oil is suitable for re-refining or requires incineration.

Typical Generators

Commercial shipping operators
Inland waterway vessel operators
Fishing fleet operators
Ferry and passenger vessel operators
Port and harbour authorities

Disposal & Valorisation Routes

Established valorisation pathways for EWC 13 04 01, ranked by economic value and market depth.

Port waste reception and oil recovery

Primary

Bilge oil and sludge is pumped to port reception facility vessels or shore-based reception tanks under MARPOL delivery procedures. Reception facility operators consolidate bilge oil and arrange onward transport to licensed waste oil processor. Consolidated bilge oil with >20% hydrocarbon content is suitable for re-refinery feed or cement kiln co-processing.

Re-refining or cement kiln co-processing

Secondary

High-grade bilge oil meeting re-refinery acceptance criteria (low water, low salt content) is processed to recover base oil. Marine bilge with high salt content from seawater ingress is directed to cement kiln co-processing as alternative fuel. Calorific value of 25–35 MJ/kg makes bilge oil economically attractive as alternative fuel.

Incineration for mixed or contaminated bilge

Backstop

Bilge oil contaminated with cargo residues, cleaning chemicals, biocides or fish oil requiring specialist destruction is incinerated in hazardous waste incinerators. Port reception facilities maintain waste acceptance criteria documentation; mixed or unknown composition waste requires incineration as precautionary management.

These are the established routes for EWC 13 04 01. 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
Service activities incidental to water transportation

Operate port waste reception facilities accepting bilge oil from vessel operators under MARPOL

02
Manufacture of refined petroleum products

Re-refine consolidated bilge oil to recover base oil for lubricant blending

03
Manufacture of cement

Co-process bilge oil as alternative fuel in cement kiln with energy and mineral recovery

04
Treatment and disposal of hazardous waste

Incinerate contaminated or mixed bilge oil not suitable for recovery

Industries That Use This Waste

Sectors that valorise EWC 13 04 01 as an input material or secondary raw material.

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