How clean is clean enough for a legacy foam system?
GuidanceDecontaminationSingapore
Old foam can leave PFAS behind after a system is drained and refilled. A cleaning programme needs a defined scope, an acceptance basis and records that follow the work from the first flush to waste collection.
When an owner drains a legacy foam system, residue can remain in the tank, concentrate pipework, proportioners and hose. Refilling the system brings the new foam into contact with those surfaces, allowing residual PFAS to carry over.
PFAS, or per- and polyfluoroalkyl substances, are found in firefighting foams such as aqueous film-forming foam (AFFF). In Singapore, the National Environment Agency (NEA) sets out the cleaning and acceptance provisions in Version 02 of its industry guideline, dated 27 March 2026.1
For the owner, the work affects outage time, waste volumes and the evidence needed at completion. An incomplete scope can leave contaminated sections untreated. Poor records can leave the owner unable to demonstrate what was cleaned or how the acceptance basis was met.
Define the scope before the outage
The starting point is an inventory of the equipment that has held foam. Table 2 identifies the systems and parts within the guideline’s cleaning scope, including pipework kept packed with concentrate. The inventory should be checked against the installation so that sections are accounted for before cleaning begins.
The foam history helps the team plan the work. It should identify what each system has contained and where that information is uncertain. Baseline samples can provide a comparison for later results; their purpose and locations should be decided before the old foam is removed.
The owner should also settle the acceptance basis and waste arrangements at this stage. Cleaning produces rinsate, the liquid collected from flushing and soaking, as well as residues and removed components. The programme needs storage capacity, a collection arrangement and a record of where those wastes go.
Apply and record the cleaning method
Section 5.2 requires companies to take all reasonable and practicable steps to clean their systems and equipment. Its hot-water method begins with continuous flushing until no foaming is visible at the outlet, followed by at least three soaking and flushing cycles of 24 to 48 h each.1
Each soak starts at 50 °C or higher, with the temperature maintained as far as practicable through the cycle. High-pressure washing or surface agitation may assist in removing solidified residue. The work record should show the equipment treated, the cycles completed and the conditions achieved.
For engineersOther methods in Section 5.2
Section 5.2 also describes cleaning with polar solvents and with chemical additives. Selection requires an assessment of cleaning effectiveness, practicality, flammability and chemical compatibility. The method and its conditions should be established for the equipment being treated before work begins.
Sampling and engineering judgement help determine where effort is needed, which components should be replaced and how the work can be sequenced. These decisions affect the outage and the volume of waste. Any reduction in repeated work must still leave the chosen cleaning method and acceptance basis satisfied.
Keep the two acceptance routes clear
Section 5.3 recognises that some PFAS may remain after cleaning. It provides two acceptance routes: residual PFAS within the Table 1 limits, or cleaning to as low as reasonably practicable (ALARP) using a method described in Section 5.2. Both sit within the requirement to take all reasonable and practicable measures to remove residues.
Footnote 4 explains that systems cleaned using at least the hot-water method, or another method described in Section 5.2, are deemed to meet the ALARP requirement and do not require re-cleaning on that basis. The completion record should identify the route relied on and the evidence supporting it.
BackgroundPFAS rebound and the one-month sample
Residual PFAS retained on internal surfaces can be released into the replacement foam after cleaning. This rebound effect means that a sample taken immediately after the work may not represent the concentration after the foam has remained in the system.
Section 5.3 allows contamination to be assessed using a representative sample of the new concentrate or foam solution after one month in the cleaned system. It does not make that sample mandatory in every case. The sampling plan and the interpretation of results should be tied to the acceptance route selected.1
Close the work with a usable record
A practical completion file brings together the component inventory, foam history, acceptance basis and cleaning records for each system. It should include baseline and subsequent laboratory results where testing forms part of the programme, together with records of waste collection and disposal.
Where laboratory testing is used, confirm the laboratory’s accreditation and the method’s suitability for the samples. Section 3.1 sets out the accreditation basis NEA accepts and gives a non-exhaustive list of recommended methods. The file should make each result traceable to its system, sample location and collection date.
For ownersQuestions to settle before work begins
- Which tanks, components and foam-filled pipe sections are in scope?
- What has each system contained, and where is the history uncertain?
- Which cleaning method and Section 5.3 acceptance route will be used?
- What evidence will demonstrate that the method was completed?
- Where will rinsate be held, and which licensed collector will take the waste?
- If testing is planned, which laboratory, method and sampling dates will apply?
- Who will assemble and retain the completion file?
At handover, the owner should be able to trace each system from its cleaning scope to the work completed, the acceptance basis and the waste records. Any unresolved items should remain identified in that file.
For engineering advice on a specific site, contact Archer.
Notes
- National Environment Agency and Oil and Petrochemical Industry Technical & Safety Committee Working Group, Industry guideline on the phase out of PFAS containing firefighting foams, Version 02, 27 March 2026, Sections 3.1, 5.1 (Table 2), 5.2, 5.3 (including footnotes 3 and 4) and 5.4. Link. ↑
- National Environment Agency, Table 1: List of controlled hazardous substances (hazardous substances listed in the 2nd Schedule of the EPMA), list updated as of 31 December 2025. Link. ↑
- Environmental Protection and Management Act 1999, Singapore Statutes Online, Second Schedule. Link. ↑
- Environmental Public Health (Toxic Industrial Waste) Regulations, made under the Environmental Public Health Act, Singapore Statutes Online. Link. ↑
- National Environment Agency, Toxic Waste Control, including the list of licensed toxic industrial waste collectors. Link. ↑
- PUB, Singapore’s National Water Agency, Trade Effluent Management (Sewerage and Drainage (Trade Effluent) Regulations). Link. Sewerage and Drainage (Trade Effluent) Regulations, Singapore Statutes Online. Link. ↑
- National Environment Agency, Allowable limits for trade effluent discharge to watercourse or controlled watercourse (Environmental Protection and Management (Trade Effluent) Regulations). Link. ↑
Director, Archer (S) Pte Ltd. Archer designs and tests fire protection for petrochemical, aviation and high-hazard industrial facilities across APAC and the Middle East.