Small-Scale Desalination and Distributed Water

Large-scale desalination produces freshwater for $0.27-0.41/m³. 2 billion people lack reliable water access. The gap between what is technically possible and what is actually deployed is institutional, not technical. Where are the opportunities for contribution?

25 min read

The Overhang

Modern seawater reverse osmosis produces freshwater for $0.27-0.41/m³ —cheaper than many municipal water systems. Energy consumption has dropped 90% in 50 years. Solar-powered systems eliminate grid dependence.

Yet 2 billion people lack reliable access to safe drinking water.

The gap is not technical. Small-scale desalination rarely fails because the salt wasn't removed. It fails because the system around the machine collapses:

  • Payment interface mismatch: Kenya's Grundfos Lifelink "Water ATMs" failed because residents didn't carry smart cards and feared data collection would lead to eviction. The high-tech solution was repurposed into tailoring shops.
  • Supply chain death spiral: Pacific island units become "graveyards"—a simple part failure leads to 6 months of downtime because there's no local supply chain.
  • Maintenance collapse: In Ghana and India, projects enter a death spiral where a minor fault stops revenue collection, which means no funds for repairs, which leads to permanent abandonment.
  • Political white elephants: Punjab, India—RO plants built for visibility but abandoned immediately because village councils couldn't pay the electricity bill.

The next breakthrough isn't a better membrane. It's a resilient business model (like Jibu's franchise) or a simplified supply chain (like standardising parts across a region).

This is classic overhang territory: the capability exists, but deployment lags because of institutional architecture, not chemistry.

Lens: I come at this as a software builder and systems generalist. I notice coordination failures, monitoring gaps, and model-to-reality friction more than I notice membrane chemistry. Treat the technical claims as sourced and the deployment hypotheses as hypotheses.


The State of Play

What's Working Now

Large-scale SWRO has matured spectacularly:

  • Sorek B (Israel): Water at $0.41/m³—cheaper than many municipal systems
  • Energy: 2.0-2.5 kWh/m³, down from 20-30 kWh/m³ in the 1970s
  • Scale: 95+ million m³/day global capacity, growing 6-12% annually

Small-scale commercial systems are proven:

  • Elemental Water Makers (Netherlands): 2.7-3.0 kWh/m³ using Danfoss iSave energy recovery, deployments across Philippines, Madagascar, Senegal
  • OSMOSUN (France): 1-20,000 m³/day modular systems, battery-free off-grid operation
  • Boreal Light WaterKiosk (Germany): 23 Kenyan hospitals, 1 million+ litres daily combined

"Water ATM" kiosk models demonstrate distributed viability:

  • Piramal Sarvajal (India): 930+ touchpoints across 16 states, serving 420,000 daily, cloud-connected IoT monitoring
  • Jibu (East Africa): Franchise model across Rwanda, Uganda, Kenya, Tanzania—100+ million litres sold in 2021
  • GivePower (Kenya): Solar Water Farms producing ~75,000 L/day per container, water at $0.0025/L

Breakthrough technologies reaching commercial deployment:

  • MIT battery-free electrodialysis: 5,000 L/day from 6-month field trial, 94% solar energy capture, commercial company launching 2025
  • Salinity Solutions HyBatch: 50% energy reduction, 98%+ recovery rates, commercial orders from Chile to Japan
  • Wave-powered desalination: Oneka ($21.4M raised) and Ocean Oasis (€6M EU funding) achieving TRL 6-7

What's Stuck: A Failure Taxonomy

Small-scale projects fail at alarming rates—but not randomly. Failures cluster into four categories, each with different solutions:

Visual summary of failure patterns. Click to enlarge. Full text version follows below.
🔍Detailed Failure Breakdown

Technical Failures (Solvable with better engineering)

  • Membrane fouling: Inorganic scaling from site-specific silica/sulfate. Biofouling from inadequate pre-treatment.
  • Battery death: Lead-acid batteries in solar-RO degrade rapidly in heat. Direct-drive attempts cause "water hammer" fatiguing components.
  • Sensor failure: Ultrasonic level controllers fail, causing pumps to run dry. Proprietary PLCs can't be bypassed by local mechanics.

These are not the main killers. Better feedwater characterisation helps, but most projects don't die here.

Operational Failures (Solvable with monitoring + maintenance networks)

  • Sole-operator burden: Mer Island's plant needed attention every 4-5 hours—unsustainable for one trained person.
  • Tyranny of distance: Yalata required technicians from 1,000 km away for minor faults. Downtime measured in weeks.
  • No remote diagnostics: Sensor failures invisible until catastrophic; no early warning.

Solution: Remote telemetry, WhatsApp alerts, regional technician networks.

Institutional Failures (Solvable with different ownership/governance)

  • Contractor abandonment: Rajasthan—57 plants abandoned when contractors left despite "seven-year maintenance" clauses (no enforcement).
  • Tanker mafia: Pakistan's DHA Cogen—private vendors profit from dysfunction, political economy opposes improvement.
  • Community vs. professional management: Pure community management "has very high failure chance" (Oxfam). Pure private without community engagement also fails.

Solution: Franchise models (Jibu), cooperative ownership (REA), hybrid professional-community operation.

Financial Failures (Solvable with different capital structures)

  • Revenue collection collapse: Minor fault leads to no revenue, no repair funds, permanent abandonment.
  • Grant dependency: Donor-funded projects with no OpEx budget.
  • Electricity disconnection: Punjab plants abandoned because Panchayats couldn't pay bills.

Solution: PAYG via mobile money, service-first models (pay for water not pumps), revolving funds for cooperatives.

The pattern is clear: technology isn't the limiting factor; implementation models determine success or failure.

Regulatory frameworks impede small-scale deployment:

  • EU Drinking Water Directive exempts systems under 10 m³/day from monitoring—but discharge permits still apply
  • No jurisdiction has streamlined "small-scale desalination permits"
  • Coastal zone management designed for industrial plants, not community kiosks
  • "Humanitarian exemptions" don't exist in standard form

The Economics Reality

Small-Scale vs. Large-Scale: Different Beasts

ScaleCost/m³EnergyTypical Application
Mega (>100,000 m³/day)$0.30-0.502.0-2.5 kWhCoastal cities
Large (10,000-100,000)$0.50-1.002.5-3.0 kWhRegional supply
Medium (100-10,000)$1.50-3.003.0-4.0 kWhSmall towns
Small (1-100 m³/day)$2.00-5.003.0-5.0 kWhVillages, hotels, islands
DIY solar still$11-65N/A (passive)Households

The 2-10× small-scale premium looks prohibitive—until you factor in distribution costs:

  • Water trucking: $5-24/m³ in remote areas
  • Pipeline infrastructure: CAPEX often exceeds 10 years of operating costs
  • Bottled water: $500-2,000/m³

When distribution requires trucking, small-scale on-site desalination often proves cheaper despite higher per-unit production costs.

Brackish vs. Seawater: The Hidden Opportunity

FactorSeawaterBrackish Groundwater
Operating pressure60-70 bar5-15 bar
Energy consumption2.5-4.0 kWh/m³0.5-2.5 kWh/m³
Membrane life3-5 years5-7 years
Relative costBaseline30-50% lower

For inland areas with saline groundwater, solar-powered brackish water RO represents the most economically viable approach. This is underserved—most R&D focuses on coastal seawater mega-plants.

Brine Management: The Scale-Dependent Reality

For mega-plants (100,000+ m³/day), brine valorisation is transformative:

NEOM's vision integrates desalination + green hydrogen + mineral recovery. At scale, plants become mineral refineries with water as byproduct. TEA simulations show net water cost of ~$0.30/m³ after mineral credits.

For small-scale (1-100 m³/day)? Mineral extraction is mostly irrelevant. You can't run selective lithium sorbents on a village system.

What matters at small scale:

ApproachComplexityCost ImpactBest For
Evaporation pondsLowMinimalArid, available land
Salt-tolerant irrigationLowBeneficial useAgricultural areas
Deep-well injectionMediumModerateSuitable geology
Tanker disposal to coastHigh$2-5/m³Inland, no alternatives

The realistic small-scale goal is cost-neutral disposal or beneficial use, not profit. Focus on simplified ZLD for small operators, not mineral extraction.


The Regulatory Landscape

Regulations were designed for large industrial plants, not community kiosks. This creates specific barriers:

World map showing desalination regulatory regimes
Click on a region to see its regulatory details
📋Full Regional Breakdown

EU/Spain

Permits required: EIA (Directive 2014/52/EU), water concession under Spanish Water Act (TRLA), discharge permits from river basin authorities (Confederaciones Hidrográficas).

Small-scale grey zone: Under 10 m³/day or under 50 persons exempted from EU Drinking Water Directive monitoring—but unclear if this applies to commercial operators. Discharge permits still required.

Brine discharge: Salinity threshold of 38.5 psu for protecting Posidonia oceanica seagrass enforced since 2006. Barcelona Convention LBS Protocol applies.

United States

The NPDES reality: Any point source discharge to surface waters requires an NPDES permit under the Clean Water Act. No federal "small-scale exemption."

Inland brine disposal: Surface discharge, POTW, or deep-well injection—all face increasing restrictions. The permit requirements for ZLD are minimal, but capital costs are prohibitive.

State variation: California's Desalination Amendment to Ocean Plan provides uniform permitting for seawater facilities. Texas has explicit landfill mining registration; no equivalent for desalination.

India

CGWA gatekeeping: Central Ground Water Authority NOC required for groundwater abstraction. Exemption for under 2 HP non-energised pumps.

Coastal zone complexity: CRZ Notification 2011 clearance required for coastal projects. District Coastal Zone Management Authority (DCZMA) approval needed.

Brine: No specific ZLD mandates for seawater desalination, but EIA studies required. Minjur plant discharges 650m offshore.

East Africa (Kenya focus)

EIA required: National Environment Management Authority (NEMA) license for coastal development. Water Resources Authority (WRA) permits for abstraction.

Humanitarian context: Desalination is considered "measure of last resort" by humanitarian agencies, but Oxfam and others have deployed 15,000-70,000 L/day solar plants with varying success.

No jurisdiction has a dedicated "Small-Scale Desalination Act" or streamlined permitting for community systems. Everywhere, small-scale is regulated through adaptation of ill-fitting industrial frameworks—like running a food truck under restaurant regulations designed for hotel kitchens.


Historical Precedents: How Water Access Transformed Before

Four historical analogies illuminate how desalination might transition from niche to ubiquitous:

1. Chlorination (1908-1925): Redefining "Pure"

The Jersey City verdict (1908) was the tipping point. Dr. John Leal installed chlorination at Boonton Reservoir without public permission. When sued, the court ruled that water is defined by what's in it (safety), not what was done to it (process).

Adoption was explosive: 53% of US urban supplies chlorinated by 1914. 85% of treatment plants by 1941. The "Mills-Reincke Phenomenon"—for every typhoid death prevented, several additional deaths averted from other causes due to improved "health stock."

Lesson for desalination: Performance-based standards. Water should be defined by what's at the tap, not where it came from. This legal framework already exists—it needs explicit application to desalination and water reuse. Create "safe harbours" for utilities meeting strict output standards regardless of source.

2. Rural Electrification (1935-1953): Cooperative Finance

The problem: 90% of urban Americans had electricity; only 10% of rural farms. Private utilities refused to serve dispersed, low-load customers.

The REA model: Not government-built infrastructure, but government financing for member-owned cooperatives.

  • 35-year loans at 2% interest (government's borrowing cost)
  • Technical assistance and standardized equipment
  • "Area coverage" mandate—profitable clusters cross-subsidise remote connections

Result: 90%+ rural electrification by 1953.

Modern proof: North Alamo Water Supply Corporation (Texas) operates brackish groundwater desalination plants (3.0 + 3.5 MGD) as a member-owned cooperative, accessing TWDB grants and low-interest loans that private developers can't.

Lesson for desalination: A "Rural Desalination Revolving Fund" with 30-40 year loans at sub-market rates, specifically targeting member-owned cooperatives and small water districts. Bypass the "high cost of capital" that stalls private development.

3. Oral Rehydration Therapy (1970s-1990s): Decentralising Production

The breakthrough: Cholera treatment decentralised from hospitals (IV drips) to households (sugar + salt + water). BRAC trained 12 million Bangladeshi mothers in home preparation.

The mechanism: Hyper-decentralisation. Production at point of consumption. Incentive alignment (workers paid on results). Standardisation ("finger standards" for salt measurement).

Impact: 50-70 million lives saved. Annual child diarrhoea deaths from ~5 million (1980) to under 500,000 today.

Modern equivalents: Jibu franchises, Sarvajal Water ATMs, GivePower kiosks. Water as "consumer good" purchased daily, not "infrastructure" from utilities.

Lesson for desalination: The "water ATM" model—decentralised, community-operated, digitally managed—is the equivalent of ORT. Focus on making the unit simple enough for local operation, standardised enough for remote support.

4. M-PESA (2007-2015): Regulatory Sandbox + Agent Networks

The regulatory innovation: Kenya's Central Bank allowed Safaricom (a telco, not a bank) to operate financial services under a "letter of no objection" rather than full banking license.

Scale: From 26% financial inclusion (2006) to 75%+ (2016). 31.8 million active users. 43% of Kenya's GDP flowed through M-PESA by 2013.

The PAYG unlock: M-PESA enabled Pay-As-You-Go financing for solar home systems (M-KOPA). Micropayments via mobile money. GSM chips allow remote disablement if payment stops. The asset becomes collateral.

Lesson for desalination: Integrate with mobile money rails. Pre-paid water meters. PAYG removes upfront cost barriers. "Water-as-a-Service" with remote monitoring and automatic billing. The off-grid solar market grew to $1.75 billion serving 420 million users—water can follow the same trajectory.

Comparative Timelines

TransformationTipping PointMass AdoptionTime to Scale
Chlorination1908 (Jersey City)~1925 (major cities)~17 years
Rural Electrification1935 (REA Act)1953 (>90% farms)~18 years
ORT1980s (BRAC)1990s (widespread)~15 years
Mobile Money (Kenya)2007 (M-PESA)2015 (>70% access)~8 years
Distributed DesalEmerging (c.2015)Projected 2030-2035In Progress

What Would Unstick This

The professional landscape is thin. Major water companies profit from mega-projects. Academic research focuses on membrane chemistry, not deployment models. Startups chase clean feedstocks, not legacy groundwater.

Bottlenecks and Leverage Points

Four systemic blockers prevent small-scale desalination from scaling:

  1. No operational intelligence layer: Plants run on proprietary PLCs with no remote diagnostics. Failures invisible until catastrophic.
  2. No accessible techno-economic modeling: Decision-makers can't evaluate feasibility without hiring consultants or running Python notebooks.
  3. No regulatory clarity for small-scale: Every jurisdiction regulates containerised kiosks through frameworks designed for industrial plants.
  4. No standardised financing for cooperatives: Private capital wants 5-year payback; community water needs 30-year patient capital.

Candidate Artifacts

These are hypothetical leverage points—things that could exist and would help. Some are software, some aren't. They're starting points for exploration, not a to-do list.

WaterTAP Companion

The Linux of Water

💻 Software

The DOE has spent millions building WaterTAP—an open-source Python library for techno-economic modelling. It's powerful. It's also CLI-driven, PhD-oriented, and has no UX. Almost no one can drive it.

Keep It Alive Ops Stack

The Android of Desalination

💻 Software

There's no "Android for Desalination." Small plants run on proprietary, clunky PLCs. When things break, no one knows until it's catastrophic. The failure analysis shows this kills projects.

Regulatory Sandbox Map

Where Can You Actually Deploy?

⚖️ Policy

Spain allows exemptions for under 10 m³/day. Kenya has "Category A" permits. Texas has General Permits for Class I wells. But no one has mapped where you can deploy without a 3-year EPA struggle.

Lower-Priority Ideas (Still Valuable)

  • Brackish Feasibility Explorer: Combine NAWI Water DAMS + Open Membrane Database + groundwater surveys into "input location to estimated cost" tool
  • Sensor Fusion for Feedwater: RGB cameras + NIR spectroscopy for water quality classification (needs hardware access)
  • Solar-Aware Control Algorithms: Prototype in Python with solar irradiance data (no hardware needed)

Reality Checks Needed

These are specific people or experiences that could quickly prove this analysis wrong. Epistemic rigor, not networking:

  • Someone who's operated a 5-50 m³/day brackish RO plant in Spain or East Africa — Could validate whether the failure taxonomy matches ground truth
  • A discharge permit officer from California EPA or Spanish Confederación Hidrográfica — Could clarify whether small-scale exemptions actually exist in practice
  • Someone who's worked on JICA-funded or World Bank water projects — Could explain what actually happens after the grant is signed
  • A WaterTAP maintainer — Could confirm whether a "lite" UX layer would be welcomed or redundant
  • An operator from Jibu, Sarvajal, or GivePower — Could validate whether the PAYG model actually works as described

If you fit any of these descriptions and think I've got something wrong, I'd genuinely like to hear from you.


Resources and Entry Points

For anyone exploring this space—not prescribing who should do what.

  • The Water Network (by AquaSPE): Largest global forum for water professionals, dedicated desalination group
  • IDRA (International Desalination & Reuse Association): 2,600+ members, Young Leaders Program
  • AEDyR (Spanish Desalination Association): €149/year membership, 300-member network, biennial Congress
  • WaterTAP GitHub: Open issues and discussions, active contributor engagement
  • LibreWater / KnowFlow: Open hardware communities, maker-oriented

Competitions and Funding

  • Waves to Water Prize (DOE): $3.3M across stages, wave-powered desal focus
  • Imagine H2O Accelerator: Zero-equity model, 85+ mentors, 2026 applications likely October 2025
  • Bureau of Reclamation DWPR: $100-400K grants, annual calls (typically September)
  • California Water Desalination Grant Program: Continuous applications, $123M+ distributed
  • Horizon Europe Mission Ocean: €120M call, September 24, 2025 deadline

Concrete First Steps

Month 1 (Embed):

  1. Clone WaterTAP, run 1-2 example models
  2. Join The Water Network, follow IDRA, join AEDyR if Spain-focused
  3. Read NAWI Master Roadmap for priority areas
  4. Post one public GitHub issue or discussion showing you understand the ecosystem

Month 2 (Build):

  1. Pick one track: modeling UX, ops intelligence, or data tool
  2. Build minimal but working prototype
  3. Publish code + README + short technical write-up

Month 3 (Connect):

  1. Share with WaterTAP maintainers, LibreWater/KnowFlow maintainers, AEDyR contacts
  2. Ask: "What would make this actually useful?"
  3. Get external user feedback, possibly first PR or collaboration

Deep Research

💀Deployment Failures: Why Projects Die

Based on multi-model research, December 2025

The Punjab and Haryana "RO Scam" (India): CAG audits revealed 19 RO plants costing ₹1.62 crore were non-functional. Money released for plants never commissioned or immediately abandoned. In Badshahpur and Dhanthal, schemes costing over ₹500 lakh became "ungainful expenditure"—plants defunct due to non-payment of electricity bills by Panchayats. The National Rural Drinking Water Programme audit documented similar patterns nationwide.

The Fundamental Pattern:

Technical Failure Modes:

  • Membrane fouling: Inorganic scaling from site-specific silica/sulfate. Biofouling from inadequate pre-treatment. Djerba autopsy showed organophosphate antiscalants reacted with aluminum, creating worse fouling than no treatment. Rajasthan membrane autopsy study documented similar issues.
  • Battery death: Lead-acid batteries in solar-RO degrade rapidly in heat. Direct-drive attempts cause hydraulic surges ("water hammer") fatiguing components. IWA review of solar-powered RO.
  • Sensor failure: Ultrasonic level controllers fail, causing pumps to run dry. Proprietary PLCs can't be bypassed by local mechanics.

Institutional Failure Modes:

  • Contractors abandon remote sites despite maintenance clauses (no enforcement) — Rajasthan: 57 plants abandoned, NIRDPR study
  • "Tanker mafia" benefits from dysfunction — Pakistan DHA Cogen, political economy opposes improvement
  • Community management "has very high failure chance" without professional support
  • Sole-operator burden: Mer Island's plant needed attention every 4-5 hours
  • Yalata, Australia: required Adelaide technicians (1,000 km) for minor faults

Pacific and Caribbean Examples:

The Lesson: Service-first models (pay for water, not pumps) + standardisation + real-time telemetry + rigorous hydrogeological assessment. See World Bank private operator models analysis.

🌍African and South Asian Context

Based on multi-model research, December 2025

India: Industrial Capability

Pakistan: Governance Failure

Bangladesh: The Micro-Scale Trap

Kenya: Modular Revolution

Senegal: West African Anchor

Financing Models:

💎Brine Valorisation: The Liquid Ore

Based on multi-model research, December 2025

What's in SWRO Brine: Standard brine: 65,000-80,000 mg/L TDS (1.8-2.2× seawater concentration).

  • Major ions: Na, Cl (85%+ by mass), Mg (3,000-3,500 mg/L), SO4, Ca, K
  • Strategic traces: Li (0.3-0.5 mg/L), Rb (0.2-0.3 mg/L), Sr (13-17 mg/L), B (8-10 mg/L)
  • Regional variation: Arabian Gulf/Red Sea brine >90,000 mg/L TDS (hyper-saline advantage)

Viable Extraction:

  • NaCl: $5-15/ton production cost, offsets disposal
  • Magnesium: $150-300/ton, EU targeting Mediterranean brine for supply security
  • Lithium: Emerging—DLE (Direct Lithium Extraction) achieving $3,500-4,400/ton, competitive with terrestrial brines
  • Rubidium: >$1M/ton but extreme selectivity needed; research-stage

Technologies:

  • HPRO/OARO for concentration beyond standard RO limits
  • Membrane Distillation for near-saturation using waste heat
  • Selective sorbents (LMO, aluminum-based, crown ethers) for Li/Rb
  • Electrochemical pumping for targeted ion extraction

Commercial Players:

  • NEOM Enowa: 500,000 m³/day ZLD + Green Hydrogen integration + "High Value Chemical" park
  • Sea4Value (EU Horizon 2020): 9 critical raw materials from Mediterranean brine
  • Salinity Solutions: Batch RO for lithium enrichment, partnered with SQM and Cornish Lithium
  • Olokun Minerals: Water-based elution, "Nano-Beads" for chemical-free extraction

The Math: 100,000 m³/day plant with full mineral recovery:

  • OPEX increases from $0.80 to $1.80/m³
  • Mineral revenue credit: ~$1.50/m³
  • Net water cost: ~$0.30/m³

Note: Brine valorisation economics are highly site-specific. The figures above are illustrative rather than universal.

⚖️Regulatory Frameworks by Jurisdiction

Based on multi-model research, December 2025

Summary Table:

RegionWater RightsEnvironmentalDischargeSmall-Scale Exemption
SpainConfederaciones HidrográficasMITECO EIARegional Water AuthorityUnder 10 m³/day DWD exemption
USState water agenciesEPA/State DEQNPDES permitGeneral permits may apply
IndiaCGWA/State GWAMoEFCC, State PCBState PCBUnder 2 HP non-energised exempt
KenyaWater Resources AuthorityNEMANEMANo specific threshold

Key Legislation:

Cross-Cutting Issues:

  • No jurisdiction mandates ZLD for small-scale
  • Humanitarian/emergency deployments lack standardised exemption frameworks
  • Community vs. commercial systems: unclear whether small privatised providers exempt under EU DWD

Key Gap: No "Small-Scale Desalination Act" exists anywhere. Projects must navigate industrial frameworks designed for 100,000+ m³/day plants.

📜Historical Transformations: Pattern Recognition

Based on multi-model research, December 2025

Common Success Factors:

  1. Crisis creates urgency: Typhoid epidemics, 1971 Bangladesh cholera, acute remittance needs (M-PESA)
  2. Technology dramatically reduces cost/complexity: Chlorination at 5.6¢/million gallons, ORT at $0.50/treatment
  3. Champions and institutional backing: Dr. John Leal (chlorination), Jim Grant (ORT/UNICEF), REA under Roosevelt
  4. Demonstration effects: Jersey City's 1908 success spread to 1,000+ cities in a decade
  5. Standardisation: REA's model Electric Cooperative Corporation Act, WHO/UNICEF ORS formula
  6. Distribution innovation: Cooperatives (REA), BRAC door-to-door training, agent networks (M-PESA)
  7. Regulatory flexibility: M-PESA's "letter of no objection" from Central Bank of Kenya

Strategic Lessons for Desalination:

Historical PrecedentLessonApplication
ChlorinationPerformance-based standardsDefine "safe water" by output, not source/process
REACooperative finance30-40 year loans at sub-market rates for community systems
ORTDecentralise to householdWater ATMs, kiosk franchises, community operators
M-PESARegulatory sandbox + PAYGMobile money integration, pre-paid meters

The Blueprint:

  • Legal tipping point: Create "safe harbour" for utilities meeting output standards
  • Financial tipping point: Revolving fund for cooperative/community ownership
  • Operational tipping point: Franchise-based, PAYG distribution for last mile
🔓Open Resources for Contributors

Based on multi-model research, December 2025

Open Software:

  • WaterTAP (NAWI): Techno-economic modeling, Python, 40+ contributors. GitHub, Documentation, NAWI Hub
  • DesalSim (TU Delft): MIT-licensed simulation for RO, NF, MED, ED, crystallizers. GitHub, 4TU Archive
  • KnowFlow: Arduino-based water quality monitor. GitHub

Open Hardware:

Open Data:

  • Water DAMS (NAWI): Datasets on water treatment technologies. NAWI Portal
  • Open Membrane Database: 650+ membranes, 14,000+ data points. Website, GitHub
  • US National Brackish Groundwater Inventory: Salinity and depth mapping via USGS

Commercial Examples (for reference):

Communities:

Conferences:

Industry Analysis:

Summary

Key findings from this investigation:

  1. The technology exists—but economics only work with renewable energy integration or distribution cost savings
  2. Implementation models determine success—not membrane chemistry
  3. Historical precedents show 15-20 year timelines from tipping point to mass adoption
  4. Open-source tooling gaps are real—modeling UX, operational intelligence, decision support
  5. The bottlenecks are institutional/financial, not technical

The next steps for this avenue are to validate the candidate artifacts through the reality checks listed above. If the failure taxonomy and leverage points hold up, some of these artifacts could become projects.

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This is part of the Avenues of Investigation series—mapping technological overhangs where motivated individuals might find leverage.