SANWESS Task Team · DWS · SALGA · WPO · WRC · UKZN · City of Cape Town

WESS Ecosystem Integration

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 category

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.

Water efficient

Low-to-no water use, with water recycled on site. Conventional sewered systems use 9–12 litres of potable water per flush.

Decentralised & modular

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.

Resource recovery

Full treatment of waste with recovery of nutrients, water and energy: the circular-sanitation model rather than treatment and disposal.

Climate resilient

Less vulnerable to drought and flood than water-dependent systems, and guided by product standards (ISO 30500, ISO 31800, ISO 24521).

A containerised WESS treatment unit on a concrete pad, with labelled screen, bioreactor and disinfection compartments, UV treatment line, filtration cabinet and rooftop solar panel
A containerised WESS installation: an on-site packaged treatment unit with screening, bioreactor, disinfection, UV and filtration stages, solar power and no sewer connection. Illustrative unit from the WPO workshop briefing.

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

National sanitation position

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:

19%of South Africans have no or inappropriate sanitation (chemical toilets, unventilated pits, buckets)
~2.8 mhouseholds still rely on VIP pit latrines with no safe sludge treatment
17%projected national water deficit by 2030 in an already water-scarce country
9–12 Lpotable water used per flush in conventional sewered systems
Inappropriate sanitation (chemical toilets, unventilated pits, buckets)No sanitation
10%20%30%40%50%Eastern Cape: inappropriate 12%, none 6%18Free State: inappropriate 13%, none 2%15Gauteng: inappropriate 6%, none 1%7KwaZulu-Natal: inappropriate 26%, none 6%32Limpopo: inappropriate 39%, none 5%44Mpumalanga: inappropriate 30%, none 5%35North West: inappropriate 27%, none 4%31Northern Cape: inappropriate 11%, none 4%15Western Cape: inappropriate 1%, none 0.4%1South Africa (national): inappropriate 16%, none 3%19ECFSGPKZNLPMPNWNCWCSA
Access to sanitation: overall backlog by province, as a share of the population. No or inappropriate sanitation stands at 19% nationally. Reproduced from DWS WSKS data (April 2023) as presented at the workshop.

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 AfricaECFSGPKZNLPMPNWNCWC
Overall sanitation status
Containment
1No sanitation backlog (DWS WSKS, Apr 2023)
2Inappropriate sanitation backlog (DWS WSKS, Apr 2023)
3Rate of sanitation delivery (backlog eradication)
Emptying and Transport
4Pit toilet emptying
5Vacuum truck / honeysucker needs
6Vacuum truck / honeysucker condition
Treatment
7WWTW design capacity utilised
8WWTW effluent quality
9WWTW staffing shortfall
Disposal and Reuse
10Wastewater sludge analysis, classification and management
11Faecal sludge analysis, classification and management
12Treated wastewater effluent reuse
Institutional Aspects
13Green Drop performance
14Sanitation staff vacancies
15Sanitation business financial status
GoodAveragePoor
The NSIP 2025 scorecard: fifteen indicators across the sanitation service chain for each province, reproduced from the workshop presentation (NSIP, 2025). Provinces: EC Eastern Cape · FS Free State · GP Gauteng · KZN KwaZulu-Natal · LP Limpopo · MP Mpumalanga · NW North West · NC Northern Cape · WC Western Cape.

Section 3

Regulatory requirements

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.

Settlement types where the standards recommend WESS

Three regulatory shifts

Prohibitions

Municipalities are prohibited from approving new or additional bulk connections to wastewater systems that lack sufficient capacity, and from distributing new bucket toilets.

Mandated acceptance

WSAs cannot unreasonably decline property developments proposing closed-system (WESS) sanitation, provided the development meets authorisation requirements.

Water Services Intermediary model

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

Applicability conditions

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

Decision pathway: s78 and MFMA s120

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.

s78 assessment in three phases

Phase 0 · Service context and readiness
Step 1 Understanding the state of the service
Phase 1 · Preparing the assessment
Step 2 Macro scoping
Step 3 Establish governance structure
Step 4 Financial preparation and budgeting
Step 5 Draft terms of reference
Step 6 Finalise ToR and proceed to procurement
Step 7 Appointment of consultant
Phase 2 · Conducting the assessment
Step 8 Inception
Step 9 Status quo and needs analysis
Step 10 s78(1): assess internal mechanisms
Step 11 s78(2): Council decisionYes — implement internal · No — explore external (Phase 3)
Phase 3 · External mechanisms, final decision and implementation
Step 12 s78(3)(a): notice to the local community
Step 13 s78(3)(b): assessment of external mechanisms
Step 14 s78(3)(c): feasibility study of the preferred mechanism
Step 15 s78(4): final decision and implementation

The s78(2) Council decision at Step 11 either confirms internal implementation or opens the external-mechanism phase. Reproduced from the SALGA workshop presentation.

Internal assessment criteria: s78(1)

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.

External mechanisms: s78(3)

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.

PPP obligations: MFMA s120 and Treasury approvals

StageWhat it validatesTiming rule
TVR IComplete feasibility study — all 8 domains addressed, value for money demonstrated, risk transfer defensible, community and labour views incorporatedBefore the "in-principle" Council vote
TVR IIADraft RFP and PPP agreement are legally soundBefore the RFP is issued
TVR IIBBid evaluation applied valuation metrics transparentlyPrior to appointing the bidder
TVR IIIFinalised PPP agreement and management plan consistent with approved feasibility and procurement parametersAt 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

Financing through the Water Partnerships Office

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.

From constrained budgets to bankable projects

Programmatic

Standardised national programmes rather than one-off deals, so each partnership is quicker and cheaper than the last.

Blended finance

Grants, concessional and commercial capital combined. Most WESS projects run the hybrid model: user charges partially cover costs, and grants subsidise the rest.

PPP structuring

Clear risk, payment and performance terms that satisfy both s120 and lenders.

Project preparation

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

De-risking the installed unit

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.

De-risking Water Efficient Sanitation Solutions: a walkthrough of the protocol, the site engagement and the live rating (WASH R&D Centre, UKZN). Watch on YouTube.
The WESS reference model: a blackwater treatment line from inlet through settling, anaerobic and aerobic biological stages to clarification; a greywater line through coagulation, ultrafiltration and ion exchange; both meeting disinfection and recirculation for flush reuse or discharge; residuals routed to sludge handling, valorisation and nutrient recovery; dots mark SenseArray-observed nodes
The reference model behind the protocol: every real WESS unit, from a household system to a 620-household community plant, is declared as a subgraph of one reference model, so a single protocol assesses them all. Dots mark sensor-observed nodes.

Site engagement

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:

Greenwithin norms: continue and monitor
Amberdrifting: an action is taken before performance is lost
Redout of specification: a confirmatory test and an operational intervention

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.

The SenseArray field logger: a compact grey box with a display panel, connected by cables to probe interfaces on a workbench
The SenseArray field logger and probe interface, assembled from commodity sensors to keep per-site cost low.
The InfraTrack dashboard: a map of South Africa with 594 registered sites as markers, and a header strip showing operational, at-risk, critical and offline counts with average measured fleet health
The InfraTrack console: the national register of 594 decentralised sites, with fleet health computed from the stored sensor stream. Provider, municipality and lender log into the same record.

Live rating

A
De-risked (Live). All criteria green, stream current and confident, no open high-severity HAZOP node; full spread benefit.
B
Watch. A criterion amber, a leading indicator tripped, or drift detected; reduced concession, provider notified.
C
Provisional. Sensor stream degraded or offline, or a laboratory round overdue; no concession, the site being unobserved.
D
Breach. A criterion red, or a high-severity HAZOP node realised; a covenant event, and the remediation window opens.

Engagement cost and financing benefit

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

Municipal implementation experience

City of Cape Town pilot implementation

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:

eThekwini reinvented-toilet pilot

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.

PRANA cost case: Portion 80 Nooitgedacht, Mogale City

PRANA WESS installation at Portion 80 Nooitgedacht: aerial view of the fenced containerised plant beside the informal settlement, and interior views of the black treatment tanks inside the container
The PRANA installation at Portion 80 Nooitgedacht, Mogale City: the fenced containerised plant at the settlement edge, and the treatment tank hall inside.
Further views of the PRANA containerised WESS plant: tank rows inside the container, the container exterior, and the electrical control cabinet
Inside the plant: tank rows, container exterior and the control cabinet. The technology is simple to install; the supporting civil works are the critical success factor.

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/dayWESSVIPsCentralizedDecentralized
Capacity (m³/day)75—150150
Total CAPEXR30 817 431R7 146 000R20 862 708R15 625 275
Annual O&MR2 016 500R1 462 500R6 006 792R7 614 775
Total cost, year 1R32 833 931R8 608 500R26 869 500R23 240 050
Cumulative, year 5R40 899 931R14 458 500R50 896 667R53 699 150
Cumulative, year 10R50 982 431R21 771 000R80 930 625R91 773 025
Cumulative, year 15R61 064 931R29 083 500R110 964 583R129 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

First steps

Drawn from across the workshop, a practical opening sequence for a WSA:

Contacts and resources

Standards & Professional RecognitionDr Preyan Arumugam

WASH R&D Centre, University of KwaZulu-Natal
[email protected]

Financing & project preparationRamona Reddy-Maduray

Programme Manager: Non-Sewered Sanitation, Water Partnerships Office
[email protected]

Institutional arrangements & s78Alana Potter

Sanitation Specialist, SALGA
[email protected]

Sanitation ecosystem & researchDr Valerie Naidoo

Water Research Commission
[email protected]

Scaling & demonstrationPhillip Majeke

Water Research Commission / WPO
[email protected]

De-risking protocolProf Randhir Rawatlal

WASH R&D Centre, University of KwaZulu-Natal
[email protected]

Department of Water and SanitationMs Tabita Napakade

Department of Water and Sanitation
[email protected]

eThekwini MunicipalityNedon Ramsuran

eThekwini Municipality
[email protected]

City of Cape TownSandile Thymoty Gqoboka

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.