inorganic test record
Nitrate and nitrite
Nitrate and nitrite are different laboratory analyses. A result supports only the analytes and reporting form listed on the report, not the source of contamination or future water safety. Confirm the units before comparing results; elevated results or infant-formula concerns need direct laboratory and local health guidance, not a calculator verdict.

- nitrate
- nitrite
Why this appears in a test plan
CDC recommends testing private wells for nitrate at least annually and when someone becomes pregnant or a child joins the household. EPA lists nitrate and nitrite among tests to consider near intensive agriculture. These are testing recommendations, not proof that a particular well is contaminated.
RHC planning: our starting panel includes nitrite alongside nitrate as an additional discussion item—not a CDC universal annual nitrite requirement. ROUTINE, SOON and URGENT are RHC next-step priorities, not medical guidance or laboratory findings. Nearby nitrogen sources and unknown new-home testing history inform discussion, not diagnosis.
What the result can tell you
A nitrate-only result does not prove nitrite was tested; a nitrite-only result does not prove nitrate was tested. A nitrate + nitrite combined result does not automatically provide two independent measurements. Interpret only the analytes and measurement form actually listed; ask the laboratory what a combined result includes.
Check the reporting basis as well as mg/L: as nitrogen (as N), as nitrate (NO3), and as nitrite (NO2) are different bases and must not be compared directly. A combined as-N result is not interchangeable with either single-analyte result. RHC advice: have the laboratory confirm the basis, method, sample location, date and relevant comparison before drawing conclusions; follow its collection instructions.
Federal public-water references in 40 CFR 141.62(b)(7)–(9) are listed below. All three are expressed as nitrogen, and the combined reference does not replace the separate nitrate and nitrite limits.
- Nitrate: 10 mg/L as N
- Nitrite: 1 mg/L as N
- Total nitrate + nitrite: 10 mg/L as N
What it cannot prove
Those federal MCLs apply to the public water systems covered by the regulation. They are not nationwide mandatory standards for every private well, a private-well compliance certificate or return-to-use permission. Specific state or local requirements may still apply; confirm them with the responsible authority.
Non-detect does not mean zero: interpretation depends on the tested analytes, method and reporting limits. EPA Region III guidance addresses analytical uncertainty, not a private-well clearance procedure. RHC planning boundary: one low result or non-detect does not establish safety for untested substances or future seasons, storms or land-use changes. Neither a concentration nor appearance identifies the contamination source or establishes overall safety.
Use the result safely
No report means the result is unknown, not safe or above a limit. With a nitrate-only, nitrite-only or combined report, confirm its actual scope; unresolved units or reporting basis require laboratory clarification, not an automatic pass/fail. For a known elevated result or infant-formula water concern, use a reliable suitable alternative for drinking and food preparation while contacting the laboratory and local health/environmental department. Do not wait to complete the recommender.
High nitrate/nitrite exposure can impair blood oxygen transport; infants, especially those under six months using formula made with contaminated water, need particular care. For suspected or identified unsafe chemical contamination, do not rely on boiling: use appropriate safe alternative water for mixing formula or ready-to-feed formula as appropriate, and follow local public-health and pediatric guidance.
If an infant has difficulty breathing or blue/purple skin or lips, seek emergency medical help immediately; do not wait for a water test or this tool. These signs do not diagnose nitrate/nitrite poisoning and need medical assessment.
Boiling does not remove nitrate/nitrite contamination and is not a safety fix. ATSDR describes both as non-volatile; Wisconsin SLH specifically warns that boiling can increase nitrate concentration through evaporation. This does not import Wisconsin requirements into a national rule.
RHC planning advice: do not assume an ordinary filter is effective. Confirm the treatment technology and its suitability for the actual contaminant with qualified professionals. Installing treatment alone does not establish safe water; confirm the appropriate post-treatment testing and follow-up with the laboratory and local authority. No single result automatically clears all uses.
Sources and review record
- CDC: Well testing: annual nitrate, pregnancy/child triggers and local follow-up (July 1, 2024)Reviewed 2026-10-13
- US EPA: Private-well testing: agriculture, laboratory reports and retestingReviewed 2026-10-13
- US EPA: Contact Information for Certification Programs and Certified Laboratories for Drinking WaterReviewed 2026-09-05
- eCFR / US EPA: 40 CFR 141.62(b)(7)–(9): public-water MCLs, all as nitrogenReviewed 2026-10-13
- US EPA: National Primary Drinking Water Regulations: public-water scopeReviewed 2026-10-13
- US EPA: Learn About Private Water Wells: state/local well conditionsReviewed 2026-10-13
- CDC / ATSDR: Nitrate/Nitrite ToxFAQs: compounds, infant risk and non-volatility (reviewed July 2017)Reviewed 2026-10-13
- CDC: Formula preparation: Chemicals in water (May 14, 2026)Reviewed 2026-10-13
- US EPA Region III: Detection-limit guidance: analytical uncertainty, not private-well clearanceReviewed 2026-10-13
- Wisconsin State Laboratory of Hygiene: Nitrate interpretation: reporting forms and boiling limitation, not nationwide state rulesReviewed 2026-10-13
- CDC / ATSDR official archive: Clinical assessment: serious symptoms need medical evaluation, not water-based diagnosisReviewed 2026-10-13