SANWESS Task Team · DWS · SALGA · WPO · WRC · UKZN · City of Cape Town
Water Efficient Sanitation Solutions are now part of South Africa's compulsory national norms and standards. This guide sets out the position for Water Services Authorities: the conditions under which WESS applies, the regulatory requirements, the s78 decision pathway, the financing routes, and the de-risking of installed units.
Compiled from the workshop Water efficient sanitation solutions — creating the ecosystem for scale-up, WISA Biennial Conference, Cape Town, 22–24 July 2026. Presenters: Dr Preyan Arumugam (UKZN WASH R&D Centre), Mr Phillip Majeke (WRC/WPO), Prof Randhir Rawatlal (UKZN), Ms Tabita Napakade (DWS), Ms Ramona Reddy-Maduray (WPO), Ms Alana Potter (SALGA), Mr Sandile Gqoboka (City of Cape Town), Dr Ashton Mpofu (Afrivolve), Dr Valerie Naidoo (WRC).
Section 1
WESS is a defined category in national regulation. The revised Compulsory National Water and Sanitation Services Norms and Standards, issued under Section 9(1) of the Water Services Act (Act 108 of 1997) and gazetted by DWS in June 2025, defines it directly:
"Water efficient sanitation solutions (WESS) means sanitation systems which require low to no water, completely off-grid, non-sewered, on-site or are decentralised and utilise technologies that include using water saving devices, water-efficient processes and beneficial use of waste products." DWS, Revised Compulsory Norms and Standards, June 2025
A WESS unit is an end-to-end system. It collects and treats waste on site to defined design parameters, recycles water for flushing or other fit-for-purpose reuse, and recovers nutrients, water and energy from by-products. The user retains a full flushing experience, served by on-site treatment rather than a sewer connection.
Low-to-no water use, with water recycled on site. Conventional sewered systems use 9–12 litres of potable water per flush.
Off-grid and non-sewered, with no bulk sewer connection and no load on strained treatment works. Rapidly deployable in dense settlements and in disaster response.
Full treatment of waste with recovery of nutrients, water and energy: the circular-sanitation model rather than treatment and disposal.
Less vulnerable to drought and flood than water-dependent systems, and guided by product standards (ISO 30500, ISO 31800, ISO 24521).
Exclusions: VIP pit latrines fall outside the category because they lack integrated safe sludge treatment. The provision or distribution of bucket toilets to communities, in formal and informal settlements alike, is prohibited.
Section 2
South Africa is not on track to meet its SDG 6 sanitation targets. The 2023–2025 planning instruments (DWS NSIP) record a backlog that continues to deteriorate under water scarcity, climate change, rapid urbanisation and population growth:
The NSIP provincial scorecards show emptying-and-transport, treatment, disposal-and-reuse and institutional indicators sitting largely in the red across almost every province. Extending conventional waterborne sewerage into that picture is often neither affordable nor physically feasible, and this is the gap the 2025 standards assign to WESS. National policy is moving away from water-intensive flush-and-forget systems, and from a treatment-and-disposal mindset, towards a circular sanitation economy in which excreta is treated as a resource for nutrients and energy.
| # | South Africa | EC | FS | GP | KZN | LP | MP | NW | NC | WC |
|---|---|---|---|---|---|---|---|---|---|---|
| Overall sanitation status | ||||||||||
| Containment | ||||||||||
| 1 | No sanitation backlog (DWS WSKS, Apr 2023) | |||||||||
| 2 | Inappropriate sanitation backlog (DWS WSKS, Apr 2023) | |||||||||
| 3 | Rate of sanitation delivery (backlog eradication) | |||||||||
| Emptying and Transport | ||||||||||
| 4 | Pit toilet emptying | |||||||||
| 5 | Vacuum truck / honeysucker needs | |||||||||
| 6 | Vacuum truck / honeysucker condition | |||||||||
| Treatment | ||||||||||
| 7 | WWTW design capacity utilised | |||||||||
| 8 | WWTW effluent quality | |||||||||
| 9 | WWTW staffing shortfall | |||||||||
| Disposal and Reuse | ||||||||||
| 10 | Wastewater sludge analysis, classification and management | |||||||||
| 11 | Faecal sludge analysis, classification and management | |||||||||
| 12 | Treated wastewater effluent reuse | |||||||||
| Institutional Aspects | ||||||||||
| 13 | Green Drop performance | |||||||||
| 14 | Sanitation staff vacancies | |||||||||
| 15 | Sanitation business financial status |
Section 3
Two instruments change the operating environment for every WSA: the June 2025 revised Compulsory Norms and Standards, and the licensing regime of the Water Services Amendment Bill, which separates the authority from the operator and enables WSAs to appoint capable, licensed providers, including the private sector.
Municipalities are prohibited from approving new or additional bulk connections to wastewater systems that lack sufficient capacity, and from distributing new bucket toilets.
WSAs cannot unreasonably decline property developments proposing closed-system (WESS) sanitation, provided the development meets authorisation requirements.
Private developers or operators deploying WESS must act as registered Water Services Intermediaries, bound by SLAs to the WSA and authorised under the National Water Act.
Combined effect: technology choice is now driven by the technical realities of population density, water scarcity and system capacity rather than by historical precedent. A WSA with treatment works over capacity may not approve further bulk connections, and a WSA presented with a compliant WESS development may not unreasonably decline it.
Section 4
WESS complements sewered sanitation across a service area rather than replacing it; hybrid approaches, with WESS and conventional systems each deployed where suitable, worked best in the pilots. WESS applies where one or more of the following conditions hold:
Market segments already demonstrated in South Africa span schools, households, informal settlements, formal housing and multi-storey developments. The demonstrations run through the SASTEP programme, with twelve school sites across six technologies plus informal-settlement and rural sites, and through municipal pilots in Cape Town, eThekwini, Johannesburg, Mogale City and Limpopo.
Section 5
A WSA holds executive authority: it must ensure access to efficient, affordable and sustainable services, plan through the IDP and WSDP, regulate locally, and decide the institutional arrangement for provision under Section 78 of the Municipal Systems Act. A Water Services Provider, internal or external, then operates the service, engages consumers and collects tariffs on behalf of the WSA.
The s78(2) Council decision at Step 11 either confirms internal implementation or opens the external-mechanism phase. Reproduced from the SALGA workshop presentation.
Each of the five criteria requires evidence rather than assertion. Costs and benefits must rest on ring-fenced financial data for the current service function; an assessment that estimates from general municipal accounts does not satisfy s78(1)(a). Capacity must be projected as well as described: the Act requires an HR plan, a costed training programme and a credible timeline. The potential for re-organisation requires structured analysis and cannot be treated as automatically satisfied. Developmental objectives require documented alignment with the current IDP and WSDP. The views of organised labour must be traceable to a formal consultation process; a notification letter to a trade union does not satisfy the requirement.
Six mechanism types must be considered: a municipal entity, another municipality, an organ of state (such as a water board), a community-based organisation, an NGO/non-profit, or a competitively tendered private-sector contract. A feasibility study that evaluates only one mechanism type cannot satisfy s78(3)(c). The study itself covers eight domains: service identification, contract term, outputs, value for money (benchmarked against the internal baseline), affordability, needs of the poor, risk transfer, and impact on staff, assets and the IDP.
| Stage | What it validates | Timing rule |
|---|---|---|
| TVR I | Complete feasibility study — all 8 domains addressed, value for money demonstrated, risk transfer defensible, community and labour views incorporated | Before the "in-principle" Council vote |
| TVR IIA | Draft RFP and PPP agreement are legally sound | Before the RFP is issued |
| TVR IIB | Bid evaluation applied valuation metrics transparently | Prior to appointing the bidder |
| TVR III | Finalised PPP agreement and management plan consistent with approved feasibility and procurement parameters | At least 60 days before contract signature |
SALGA guidance: s78 and MFMA s120 are best run as one integrated process from the outset. Municipalities that run them sequentially add months and risk producing two inconsistent feasibility documents. A feasibility study not designed to meet TVR I requirements is returned by National Treasury for rework. Stages cannot be combined or fast-tracked, and a contract executed without completing all four stages is unenforceable.
Section 6
Municipalities often lack the funds and expertise to prepare bankable projects, while banks, pension funds and corporate social investment capital stand ready to invest. The Water Partnerships Office (WPO) closes this gap. It is a ring-fenced national entity housed in the DBSA and owned by DWS, with SALGA connecting the programme to municipalities; the steering committee is chaired by the Director-General: DWS.
Within the WPO, the NSS Programme develops and scales off-grid sanitation (non-sewered sanitation, WESS and reinvented toilet technologies) through demand mapping, policy and advocacy, and the packaging of bankable projects.
Standardised national programmes rather than one-off deals, so each partnership is quicker and cheaper than the last.
Grants, concessional and commercial capital combined. Most WESS projects run the hybrid model: user charges partially cover costs, and grants subsidise the rest.
Clear risk, payment and performance terms that satisfy both s120 and lenders.
Packaging municipal projects to a fundable, investable stage, a capacity most WSAs lack in-house.
Credit enhancements from development-finance partners de-risk projects so commercial lenders can participate: first-loss and subordinated facilities, tenor extension to match infrastructure life, and guarantee products. The same toolkit secured R4.23 billion (≈USD 235 m) in grant and concessional funding from the Green Climate Fund for the Water Reuse Programme, the blueprint now applied to NSS and WESS, and has mobilised over R50 million for the sanitation programme.
The working arrangement is that a municipality brings its WESS projects to the WPO, the WPO packages them into a bankable programme, and blended finance mobilises the capital.
Section 7
Certification establishes that a design can perform under standard test conditions. It carries no statement about a particular installation, its loading, its operator, or its current month of operation, and a unit that meets design criteria on commissioning day drifts as loading, temperature, power supply and maintenance vary. A lender, a municipality and a household each need a statement about one particular installation at one particular time.
The WESS Engineering De-Risking Protocol (WASH R&D Centre, UKZN) supplies that statement: the conversion of a site from a state of uncertainty to a state of documented, monitored and managed risk, maintained as a live, financeable signal. The protocol runs alongside certification rather than replacing it.
Three visits over twelve to sixteen weeks (baseline, mid-point and final) apply eight field diagnostics on one decision tree, covering settling, hydraulics, sludge, biological activity, water quality, disinfection, product yield and microbial profiling. Every measurement resolves to a traffic light with a defined corrective move:
Seven completion criteria (effluent quality, process integrity, infrastructure, operator capability, sensor coverage, social acceptance and product-water yield) roll the compartment results up to the whole unit, alongside a living HAZOP register scored on a 5×5 severity–likelihood matrix. A low-cost sensor package (SenseArray) streams pH, dissolved oxygen, temperature, turbidity, conductivity, TDS and ORP to the InfraTrack data platform, where soft-sensor models estimate the expensive compliance parameters between laboratory rounds. The platform carries a national register of 594 decentralised treatment sites.
A full three-visit engagement costs R175 000 per site, covering engineering personnel, laboratory analysis, the sensor package with first-year telemetry, travel, consumables and reporting. Under the WESP De-Risking Fund the cost is met 50/50, so the provider carries about R87 500. On an illustrative R3 million loan over five years, a rating that moves pricing from prime (11.5%) to prime − 3 percentage points saves about R265 694 in interest, a net benefit of about R178 000 after the provider's share. Break-even sits at about one percentage point of spread.
For a municipality the same record shows that the service it is accountable for is being delivered, and gives warning of drift before failure rather than when residents report discoloured water at the toilet.
Section 8
The City of Cape Town ran WESS pilots across schools, industrial complexes, formal housing and informal settlements, with a dedicated PMU, an M&E framework with independent evaluation and go/no-go gates, and a tranche-based, incremental approach to scale-up. The lessons reported by the City:
Three demonstration sites in informal settlements, live since 2024, treat and reuse wastewater for flushing with no sewer link and no load on strained treatment works. This is the delivery model the NSS Programme scales nationally.
A life-cost assessment for a 5 000-user settlement (25 000 flushes per day) compared a WESS solution against VIPs and conventional centralized and decentralized waterborne systems:
| 5 000 users · 25 000 flushes/day | WESS | VIPs | Centralized | Decentralized |
|---|---|---|---|---|
| Capacity (m³/day) | 75 | — | 150 | 150 |
| Total CAPEX | R30 817 431 | R7 146 000 | R20 862 708 | R15 625 275 |
| Annual O&M | R2 016 500 | R1 462 500 | R6 006 792 | R7 614 775 |
| Total cost, year 1 | R32 833 931 | R8 608 500 | R26 869 500 | R23 240 050 |
| Cumulative, year 5 | R40 899 931 | R14 458 500 | R50 896 667 | R53 699 150 |
| Cumulative, year 10 | R50 982 431 | R21 771 000 | R80 930 625 | R91 773 025 |
| Cumulative, year 15 | R61 064 931 | R29 083 500 | R110 964 583 | R129 846 900 |
WESS costs more in year one and breaks even within the first five years, saving an estimated R49 m against centralized and R69 m against decentralized waterborne solutions over the project lifespan. The saving derives from very low annual maintenance cost and reduced water consumption.
Section 9
Drawn from across the workshop, a practical opening sequence for a WSA:
WASH R&D Centre, University of KwaZulu-Natal
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Programme Manager: Non-Sewered Sanitation, Water Partnerships Office
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Sanitation Specialist, SALGA
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Water Research Commission
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Water Research Commission / WPO
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WASH R&D Centre, University of KwaZulu-Natal
[email protected]
Department of Water and Sanitation
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eThekwini Municipality
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City of Cape Town
[email protected]
Training materials for every module (presentations, factsheets and supplementary reading) are freely downloadable from the WESS training library: trainingonwess.creation.camp/library. SASTEP demonstration programme: sastep.org.