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Technical Documentation

Assessment Methodology

Document
SF-AM-001
Revision
1.0
Published
June 2026
Status
Current

1.Scope

This document describes how SymbioFlows waste valorization assessments are produced. An assessment identifies the recoverable waste streams at an industrial facility, classifies each stream against the European waste classification framework, and assigns a qualitative recovery tier reflecting the maturity and accessibility of established recovery routes.

The assessment is deliberately scoped to classification and recovery potential. Ranked receiver matching, regulatory compliance screening, and freight modelling are performed by the full SymbioFlows matching engine under a commercial engagement and are outside the scope of this document.

2.Data sources

Assessments draw on the following published sources:

  • EU List of Waste — Commission Decision 2000/532/EC as amended by Decision 2014/955/EU. All six-digit waste codes referenced in an assessment are sourced from the consolidated official list (842 entries), including absolute and mirror hazardous entries.
  • Waste Framework Directive — Directive 2008/98/EC, in particular the Annex II recovery operations (R1–R13) used to characterize recovery routes, and the waste hierarchy used to order them.
  • Hazard property framework — Commission Regulation (EU) No 1357/2014 (hazard properties HP1–HP15) for the interpretation of hazardous entries and mirror-entry boundaries.
  • Published industry benchmarks — sector-level waste arisings and typical material-recovery rates from publicly available industry and regulatory publications, used to cross-check declared volumes for plausibility.

3.Stream classification process

Each declared waste stream passes through the following sequence:

  1. Stream identification. The facility's declared process steps and waste arisings are decomposed into discrete streams. Streams below a materiality threshold are recorded but not assessed.
  2. EWC classification. Each stream is mapped to a six-digit code in the EU List of Waste, resolving chapter (source activity), sub-chapter (process), and entry. Mirror entries are flagged where hazard status depends on composition.
  3. Physical and compositional profiling. The stream's physical state, dominant material fraction, and known contaminants are recorded from declared data and sector norms.
  4. Benchmark cross-check. Declared volumes are compared against published sector benchmarks; material deviations are flagged in the assessment rather than silently adjusted.

4.Recovery tier mapping

Each classified stream is assigned one of four qualitative tiers. Tiers are a function of the existence and maturity of recovery operations (Annex II R-codes) applicable to the stream, the concentration of the recoverable fraction, contamination risk, and the maturity of the receiving market.

TierMeaning
HighEstablished recovery routes with mature receiving markets; minimal pre-treatment required.
MediumViable recovery routes exist but depend on composition thresholds, pre-treatment, or regional processing capacity.
LowRecovery is technically constrained; the realistic opportunity is treatment-cost reduction rather than material recovery.
Disposal liabilityNo viable recovery route under current conditions; the stream is a managed disposal obligation.

Tier assignments are qualitative by design. The assessment does not attach monetary values to individual streams; valuation requires composition confirmation and receiver-side pricing, which sit with the full engine engagement.

5.Limitations

The assessment is a desk-based analysis and carries the following limitations:

  • It is produced from declared data and sector norms. No site sampling, laboratory analysis, or physical audit is performed.
  • Tier assignments for mirror entries are indicative pending compositional confirmation of hazard status.
  • EWC codes stated in the assessment support classification discussion; they do not constitute a regulatory waste classification, consignment documentation, or duty-of-care transfer paperwork.
  • The assessment is not an offer to broker, purchase, or accept any waste stream, and contains no receiver identities or commercial terms.

6.Reference assessment

The exhibit below is a complete assessment rendered in the delivered format, populated with representative data for an anonymized mid-size metal surface-treatment facility. Stream volumes, codes, and tier assignments are illustrative of a typical engagement in this sector.

Exhibit 6.1 — Reference assessment (representative data)

Waste Valorization

Strategic Opportunity Assessment

Reference Facility — Metal Surface Treatment

Metal finishing & surface treatment
~105 tonnes/month
June 1, 2026

5

Recoverable Streams

Identified in your waste

850

Tonnes/Year Divertable

From landfill

68%

Diversion Rate

Waste to value

Executive Summary

Strategic Analysis for Reference Facility — Metal Surface Treatment

Our comprehensive analysis of Reference Facility — Metal Surface Treatment's waste streams reveals substantial untapped value and strategic opportunities for circular economy integration.

This assessment draws on verified industry benchmarks and typical material-recovery rates to identify Metal finishing & surface treatment-specific opportunities that align with Reference Facility — Metal Surface Treatment's operational profile. Our methodology combines published benchmark data, regulatory context, and circular economy best practices to deliver actionable recommendations.

Material Analysis

High-Value Waste Stream Opportunities

Ferrous filings and turnings (EWC 12 01 01)

High Priority
High Recovery Potential

420 tonnes/year

Opportunity

Direct secondary raw material for steelmaking. A clean, segregated fraction routes to scrap processors with minimal pre-treatment; contamination with cutting fluids is the main downgrade risk.

Spent pickling acid (EWC 11 01 05*)

Medium Recovery Potential

310 tonnes/year

Opportunity

Hydrochloric pickling liquor is a candidate for acid regeneration or iron chloride recovery. Routing depends on free-acid concentration and dissolved metal load, confirmed by laboratory analysis.

Metal hydroxide filter cake (EWC 11 01 09*)

Medium Recovery Potential

280 tonnes/year

Opportunity

Filter cakes with elevated nickel or zinc content can qualify for hydrometallurgical metal recovery. Below threshold concentrations, stabilization and controlled disposal remain the default route.

Aqueous rinsing liquids (EWC 11 01 11*)

Low Recovery Potential

190 tonnes/year

Opportunity

High-volume, low-concentration stream. Recovery is limited to water reuse after on-site treatment — primarily a treatment-cost reduction opportunity rather than a material recovery pathway.

Metallic packaging (EWC 15 01 04)

High Recovery Potential

40 tonnes/year

Opportunity

Clean steel drums and metal packaging follow the standard scrap route. Drums previously holding hazardous contents require certified cleaning before reclassification.

Strategic Opportunities

Pathways to Value Creation for Reference Facility — Metal Surface Treatment

Circular Economy Integration

Transform waste streams into input materials for other industrial processes, creating closed-loop systems that reduce costs and environmental impact.

Timeline: 6-12 months

Carbon Credit Generation

Monetize carbon footprint reductions through verified carbon credit programs, creating additional revenue streams while advancing sustainability goals.

Timeline: 3-6 months

Supply Chain Optimization

Connect with industrial partners who can utilize your waste streams as raw materials, creating symbiotic relationships that benefit all parties.

Timeline: 1-3 months

Methodology or assessment enquiries

For questions on classification methodology, data sources, or to commission an assessment for a specific facility, contact our team. Response within one business day.

Request an Assessment

Or write to our team directly: info@symbioflows.com