As demand for sustainable water supply strategies accelerates, water reuse is transitioning from an experimental concept to a national priority. A new 2025 forecast estimates that $47.1 billion will be invested in municipal water reuse infrastructure across the U.S. over the next decade [Bluefield Research, 2025].

This investment surge reflects several intersecting forces:

  • Declining freshwater availability due to climate variability and drought
  • Rising demand from population growth and industrial expansion
  • Increasing pressure to reduce effluent discharge and adopt circular water strategies
  • Tightening public health regulations targeting emerging contaminants and residual risk

As water reuse projects multiply, engineers and utilities face a critical design question: What treatment processes can reliably manage complex, variable water qualities, while meeting evolving regulatory and operational constraints?

The answer increasingly points to ozone and ozone-based advanced oxidation processes (AOPs). At Pinnacle Ozone Solutions, we believe ozone should be at the core of next-generation reuse systems, for technical, operational, and environmental reasons.

Understanding the Challenge: What Reuse Systems Must Treat

Water reuse systems, whether indirect potable reuse (IPR), non-potable recycling, or industrial repurposing, typically draw from secondary effluent or tertiary-treated wastewater. These waters contain a challenging mix of contaminants:

Contaminant Category Common Targets
Dissolved Organics (DOC/TOC) Color, taste/odor, THM precursors
Pathogens Viruses (e.g., enteric, norovirus), protozoa (Giardia, Cryptosporidium), bacteria (E. coli)
Micropollutants Pharmaceuticals, hormones, PFAS precursors, industrial residues
Nutrients & Reduced Compounds Ammonia, nitrite, hydrogen sulfide
Aesthetics Geosmin, MIB, color, turbidity

 

Many of these constituents are refractory, not well removed by conventional treatment processes like chlorination, filtration, or activated sludge.

Ozone and AOP: A Multi-Function Engineered Solution

Ozone (O3) is a triatomic form of oxygen with a high oxidation potential (2.07 V). When applied to water, ozone reacts with a wide range of contaminants through:

  1. Direct oxidation — reacting with electron-rich sites (e.g., aromatic rings, double bonds)
  2. Indirect oxidation — forming hydroxyl radicals (·OH) via reaction with hydrogen peroxide or under specific pH and alkalinity conditions

This dual mode enables ozone to:

  • Disinfect pathogens with high CT efficiency (faster than chlorine or UV)
  • Oxidize organic carbon, improving UV transmittance and reducing DBP precursors
  • Break down micropollutants such as carbamazepine, sulfamethoxazole, estradiol
  • Convert ammonia and nitrite to nitrate or nitrogen gas
  • Eliminate color and odor-causing compounds, improving aesthetic quality

In AOP configurations (O3 + H2O2 or O3 + UV), oxidation potential increases to ~2.8 V via hydroxyl radical production, enabling destruction of highly persistent compounds.

Performance Benchmarks: Ozone in Reuse Applications

Field and pilot studies consistently demonstrate ozone’s efficacy in reuse treatment:

Compound Ozone Removal Efficiency (%) Notes
Carbamazepine (anticonvulsant) 95–98% High direct oxidation reactivity
Sulfamethoxazole (antibiotic) 70–90% Enhanced with AOP
Estradiol / EE2 (hormones) 85–95% Reduces estrogenic activity
Geosmin / MIB (T&O) 95–99% Fast-acting oxidation
Ammonia → Nitrate 60–85% Depends on pH, dose, and CT
Viruses (e.g., Norovirus) 4–6 log CT credit > UV

Sources: von Gunten (2003), Snyder et al. (2007), WRF #4767, Pinnacle field data (2021–2024)

Engineering Considerations for Reuse System Integration

Designing ozone for reuse treatment requires precision engineering:

  1. Mass Transfer and Contact Time
  • Pinnacle systems use pressurized injection and contactors designed to achieve >95% mass transfer efficiency
  • Typical CT values (mg·min/L) are calculated based on temperature, pH, and target pathogen/inactivation goals
  1. Instrumentation and Control
  • Integrated ORP, dissolved ozone, UVT, and flow sensors
  • Automated dosing based on influent quality and process feedback
  • Safety interlocks to prevent overdosing or residual breakthrough
  1. Materials and Construction
  • Corrosion-resistant materials: 316L SS, PTFE, PVDF
  • Seals and valves rated for ozone (Viton, Kalrez)
  • Gas-tight piping, destruct units for off-gas
  1. Modular Architecture
  • Pinnacle’s QuadBlock® ozone generators scale from <1 lb/day to >500 lb/day
  • Skid-mounted systems enable rapid deployment and plug-in integration
  • Designed for retrofit or greenfield implementation
  1. AOP Compatibility
  • Optional integration with H2O2 dosing or UV reactors for enhanced oxidation
  • Flexible switching between ozone-only and AOP mode based on contaminant profile 

Use Case Snapshot: Ozone for IPR Pretreatment (20 MGD Facility)

Challenge: Remove color, taste/odor, trace organics, and pathogens in tertiary effluent prior to BAC and UV polishing.

Pinnacle System:

  • 30 lb/day ozone generation
  • Dual-stage pressurized injection
  • Online ORP, ozone residual, and UVT monitoring
  • O3 + H2O2 AOP mode during seasonal pharmaceutical spikes

Results:

  • UVT improved from 74% → 88%
  • Geosmin/MIB below detection
  • TOC reduced by 65%
  • No ozone residual downstream of BAC
  • Compliance with IPR microbial and chemical targets

Conclusion

The projected $47.1 billion investment in U.S. water reuse is not just a policy trend; it reflects a technical shift toward higher performance, lower impact, and more adaptive treatment strategies.

Ozone-based oxidation offers the rare combination of:

  • Broad-spectrum contaminant control
  • High-efficiency pathogen disinfection
  • Residual-free, sustainable treatment
  • Scalable, compact, and automation-ready systems

At Pinnacle Ozone Solutions, we design systems engineered specifically for the next generation of reuse. Whether you’re planning non-potable, indirect potable, or industrial water recycling, our ozone and AOP platforms deliver treatment confidence, with the data to back it up.

 


 

Technical References

  • Bluefield Research (2025). U.S. Water Reuse Infrastructure Market Outlook.
  • von Gunten, U. (2003). Oxidation Reactions of Ozone in Water Treatment. Water Research.
  • Snyder, S. et al. (2007). Ozone for Trace Organics in Potable Reuse. WRF.
  • Langlais, Reckhow & Brink (1991). Ozone in Water Treatment: Engineering Applications.
  • Pinnacle Project Logs (2021–2024). Advanced Oxidation for Reuse Facilities.
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