♻️ PD CLC/TS 50625 is a series of technical specifications published by BSI as Published Documents, implementing the CLC/TS 50625 family developed by CENELEC. The series defines minimum environmental and technical requirements for the collection, logistics and treatment of waste electrical and electronic equipment (WEEE). It is the key standardization vehicle supporting the EU WEEE Directive (2012/19/EU) and national implementing legislation, enabling resource recovery while controlling pollution. The two parts in this batch are Part 3-1, which sets the general requirements for de-pollution, and Part 3-2, which gives a dedicated technical specification for lamp products containing mercury and other hazardous substances. Both were prepared under the CENELEC electrotechnical environment committee (UK committee GEL/111) and are classified under ICS 13.030.99, 29.100.01 and 31.220.01 (Part 3-2 additionally 29.140.01).
💡 The core logic of WEEE treatment is “de-pollute first, then recover”: hazardous components such as mercury in lamps, PCB in capacitors, and batteries must be removed before shredding, sorting and smelting. The quality of this de-pollution step directly controls the purity of recovered materials and the environmental compliance of the treatment facility.
1. Scope and General Framework 📌
The series follows a “general — product-specific” structure typical of CENELEC electrotechnical environmental standards. Part 3-1 states the general requirements for de-pollution applicable to all types of WEEE, while Part 3-2 builds on Part 3-1 and gives refined technical specifications for lamp-type products. Both documents are technical specifications (TS), which CENELEC members are required to announce at national level; conflicting national standards may be kept in force in parallel — therefore users should verify which requirements apply in their jurisdiction.
| Document | Part | Subject | Year |
| PD CLC/TS 50625-3-1:2015 | Part 3-1 | Specification for de-pollution — General | 2015 |
| PD CLC/TS 50625-3-2:2016 | Part 3-2 | Technical specification for de-pollution — Lamps | 2016 |
⚠️ Do not confuse the de-pollution parts with other parts of the CLC/TS 50625 family that address other stages of the WEEE chain. Always quote the exact part number so that general treatment requirements are not mistakenly applied to lamps, or vice versa.
2. De-pollution Monitoring: Target Value and Mass Balance 🔬
De-pollution effectiveness cannot be judged qualitatively. Part 3-1 provides a framework for quantifying and monitoring de-pollution through two principal methodologies:
- Target value methodology: specific target values are set for particular pollutants; compliance is checked by measuring treated materials or process data against the targets. It suits pollutants that can be measured quantitatively and where objectives are well defined.
- Mass balance methodology: the mass of pollutants entering the treatment process is balanced against the pollutant masses in the output streams (recovered materials, residues, emissions). It evaluates where hazardous substances go and how efficiently they are removed — particularly useful when direct sampling of flowing or mixed materials is impractical.
The two methods are complementary: the target value method checks whether results meet goals, while the mass balance method checks whether material flow is closed and traceable. Treatment operators may apply one or combine both depending on product type, data availability, and regulatory expectations.
💡 Practical guidance: for products with characteristic pollutants — mercury in lamps, lead in glass, brominated flame retardants in plastics — use the target value method as the primary acceptance criterion and the mass balance method as a verification and optimization tool for the treatment process.
3. Lamp-Specific De-pollution Technical Specification 💡
Part 3-2 (2016) addresses lamp-type WEEE, whose central de-pollution challenge is the safe capture and disposal of mercury. Lamp products in scope include linear fluorescent lamps, compact fluorescent lamps (CFLs), high-pressure mercury lamps and sodium lamps, all of which can contain mercury, lead-containing glass and phosphor coatings. The specification sets out directional requirements covering:
- Enclosed, negative-pressure processing: crushing, separation of mercury and phosphor should be performed in an enclosed negative-pressure environment to prevent mercury vapour and dust escaping, with exhaust gas purification and adsorption;
- Mercury and phosphor recovery: physical separation of glass, metal end caps, phosphor and mercury-bearing fractions by crushing, air classification, screening and magnetic separation; mercury-bearing material is passed to licensed deep treatment such as distillation;
- Traceability of outputs: the mass and destination of each output stream should be recorded so hazardous substances do not enter general recycling or landfill;
- Residue disposal: non-recoverable hazardous residues must be collected, stored and disposed of according to hazardous waste requirements.
🚨 Lamp de-pollution is a high-risk, high-value operation: mercury vapour and dust are hazardous to operators and the environment. Personal protective equipment and occupational health requirements apply, and lamps must never be broken in an open environment.
4. Engineering and Operational Practice 🛠️
- 🔍 Process design: waste-treatment operators should classify incoming material (mercury lamps, other luminaires, mixed electronics) and sequence the process as “de-pollution → crushing and separation → resource recovery”, keeping de-pollution separate from general crushing.
- 📊 Data recording: maintain records of incoming material, throughput, and the mass and destination of each output stream — the data basis for both the target value and mass balance monitoring approaches and for audits and certification.
- 🧪 Sampling and testing: sample and test treated material according to the selected methodology, focusing on mercury content and phosphor recovery rate; use accredited laboratories where required.
- 📋 Regulatory alignment: facilities must hold the relevant waste permits, hazardous-waste transfer documentation, and occupational health and environmental discharge approvals, and integrate with producer responsibility organizations (PROs) and collection schemes.
5. Frequently Asked Questions ❓
❓ Q: Is PD CLC/TS 50625 mandatory?
A: As a Published Document it is a technical specification without direct legal force. However, its technical content underpins compliance with the EU WEEE Directive and UK legislation, and it commonly becomes binding through regulation, permits, or contractual obligations.
❓ Q: When should I choose the target value method versus the mass balance method?
A: Use the target value method when the pollutant is measurable and the target is clear — it gives direct pass/fail results. Use the mass balance method to assess complex material flows, cases where direct sampling is difficult, or to evaluate overall pollutant removal efficiency. Combining both is recommended in practice.
❓ Q: Why must lamp de-pollution be performed in an enclosed environment?
A: Lamps contain mercury; open crushing releases mercury vapour and dust. Enclosed negative-pressure processing with exhaust purification contains the hazard, which is the central requirement of the lamp-specific specification.
🔍 Q: Can glass and metal from de-polluted lamps still be recycled?
A: Yes. The purpose of de-pollution is to first remove mercury, phosphor and other hazardous substances so the remaining glass and metal end caps become relatively clean recyclable material for the glass and metal recycling chains.