Arsenic Treatment in Private Wells: Technical Reference
This section covers treatment mechanisms, certification requirements, water chemistry considerations, performance validation, and maintenance protocols for arsenic removal in private well water systems. For a full overview of arsenic occurrence, health effects, and regulatory context, see the arsenic contaminant guide.
Primary Treatment Mechanisms
Arsenic in groundwater occurs predominantly in two oxidation states: arsenite (As(III)) and arsenate (As(V)). Arsenate is more readily removed by most treatment technologies. Arsenite typically requires pre-oxidation — using chlorine, potassium permanganate, or aeration — to convert it to arsenate before effective removal can occur.
Proven removal technologies include:
- Reverse Osmosis (RO): Pressure-driven membrane separation. Effective against both arsenate and, to a lesser degree, arsenite. Rejection rates for arsenate typically exceed 95% under standard operating conditions.
- Activated Alumina (AA): Adsorption-based media. Highly effective for arsenate removal. pH-sensitive; optimal performance occurs between pH 5.5 and 6.0.
- Iron-Based Media: Adsorbs arsenate via ligand exchange. Effective over a broader pH range than activated alumina. Competing anions (phosphate, silica, vanadium) can reduce capacity.
- Coagulation/Filtration: Used in larger systems; less common at the point-of-use (POU) or point-of-entry (POE) scale for private wells.
NSF/ANSI Certification Requirements
Certification is the primary assurance of a system's performance claim. Two standards govern arsenic treatment products at the residential scale:
- NSF/ANSI 58: Governs RO systems. Requires testing and certification of contaminant reduction claims, including arsenic (As(V) and, in some certifications, As(III)), structural integrity, and material safety. All three recommended systems carry NSF/ANSI 58 certification.
- NSF/ANSI 53: Governs activated carbon and other media-based systems making health-effects reduction claims. The Pioneer Whole-House Lead, Cyst & PFOA/PFOS Removal System ($1,669) carries both NSF/ANSI 53 and NSF/ANSI 58 certifications, providing broader contaminant coverage appropriate for high-risk installations.
Installers and specifiers should verify that the specific arsenic reduction claim — not just general certification — appears on the manufacturer's NSF product listing at info.nsf.org.
Water Chemistry Factors Affecting Performance
Arsenic removal efficiency is sensitive to several source water parameters. A full water chemistry panel should be completed before system selection. Key variables include:
- pH: Elevated pH (above 7.5) reduces RO membrane rejection rates for arsenite. Activated alumina performance degrades above pH 8.0.
- Total Dissolved Solids (TDS): High TDS increases osmotic pressure against the RO membrane, reducing flux and requiring higher operating pressure to maintain throughput.
- Competing Anions: Phosphate, silica, fluoride, and vanadium compete with arsenate for adsorption sites on media-based systems. Elevated concentrations of these anions reduce effective capacity and service life.
- Iron and Manganese: Concentrations above 0.1 mg/L can foul RO membranes or media beds. Pre-treatment filtration is required when these constituents are elevated.
- Arsenic Speciation: If source water contains significant As(III), pre-oxidation must be incorporated upstream of the primary treatment unit. Without speciation data, assume As(III) is present and design accordingly.
- Hardness: Hard water accelerates membrane scaling. Anti-scalant dosing or softening pretreatment may be required for RO systems above 7 grains per gallon (120 mg/L as CaCO₃).
Performance Tiers and Application Guidance
Minimum
The APEC ROES-50 Essence 5-Stage Reverse Osmosis System ($277, NSF/ANSI 58) is appropriate where influent arsenic is detectably above background but remains below the EPA Maximum Contaminant Level (MCL) of 10 µg/L, source water chemistry is not complex, and the installation is a standard point-of-use kitchen application. This system meets minimum certification requirements for arsenic reduction claims under NSF/ANSI 58.
Typical
The American Made Reverse Osmosis System ($628, NSF/ANSI 58) represents the standard specification for residential well treatment. It is appropriate for arsenic concentrations near or moderately above the 10 µg/L MCL, with standard water chemistry. Higher-grade components and longer membrane life reduce lifecycle cost compared to entry-level systems.
High-Risk
The Pioneer Whole-House Lead, Cyst & PFOA/PFOS Removal System ($1,669, NSF/ANSI 53/58) is the appropriate specification when arsenic concentrations significantly exceed the 10 µg/L MCL, when vulnerable occupants (infants, pregnant women, immunocompromised individuals) are present, or when co-occurring contaminants — including lead, cysts, PFOA, or PFOS — are detected or suspected. Whole-house POE installation ensures treated water at all points of consumption and dermal contact.
Performance Validation
Installation of a certified system does not guarantee in-situ performance. Validation testing is required to confirm efficacy under actual operating conditions:
- Collect paired influent and effluent samples within 30 days of system startup.
- Submit samples to a state-certified laboratory using EPA Method 200.8 or equivalent for arsenic speciation if needed.
- Target effluent concentration: below 10 µg/L (EPA MCL); below 5 µg/L is achievable and preferable for vulnerable households.
- Retest annually, and immediately following any change in source water conditions, pressure loss, or filter replacement.
Maintenance Protocols
Performance degradation in RO systems typically manifests as increasing TDS passage through the membrane. Establishing a maintenance schedule tied to water volume processed — rather than calendar time alone — improves reliability:
- Sediment and carbon pre-filters: Replace every 6 months, or sooner if pressure drop across the system exceeds 15 psi from baseline.
- RO membrane: Replace every 24 to 36 months under typical residential use conditions. High TDS or iron in source water shortens membrane life.
- Post-carbon polishing filter: Replace annually.
- Media-based systems (activated alumina, iron media): Monitor effluent arsenic concentration quarterly. Bed exhaustion is not visible — only effluent testing confirms remaining capacity. Regeneration (for AA) or media replacement schedules should be set by the manufacturer's throughput specifications, adjusted for actual influent concentration and competing anion load.
- Whole-house POE systems: Follow manufacturer-specified backwash cycles. Inspect housings and connections semi-annually for microbial contamination points.
For regulatory context, health effects data, and MCL reference information, see the arsenic contaminant guide.