Contaminant Guide

Nitrate in Well Water

Nitrate is one of the most common well water contaminants in agricultural areas of the Midwest and Mid-Atlantic, entering groundwater from fertilizers, livestock waste, and septic systems. At high levels it is acutely dangerous to infants under six months old and is classified as a probable human carcinogen from chronic adult exposure.

What is nitrate?

Nitrate (NO₃⁻) is a naturally occurring ion that becomes a groundwater concern when human activity increases its concentration in soil. It is colorless, odorless, and tasteless. Unlike many contaminants, nitrate does not build up in the body — it affects health by interfering with oxygen transport in blood.

How does it get into well water?

Nitrate moves readily through soil into shallow, unconfined aquifers. Primary sources:

  • Agricultural fertilizers (corn and soybean fields across the Midwest)
  • Concentrated animal feeding operations and manure application
  • Septic system leachate — a significant source in suburban and rural areas
  • Lawn fertilizers in high-density residential areas

Wells at highest risk are shallow (under 100 ft), located in agricultural watersheds, or near septic systems. Deep bedrock wells are generally lower risk unless there is a direct pathway from the surface.

How common is it?

Nitrate above 10 mg/L is the most frequently detected MCL exceedance in U.S. private wells. It is most prevalent in Iowa, Illinois, Indiana, Nebraska, Kansas, Minnesota, Wisconsin, Ohio, Missouri, and Pennsylvania — the heart of the Corn Belt. USGS surveys suggest roughly 4% of domestic wells nationwide exceed the MCL.

Health effects

Infants under 6 months: methemoglobinemia (blue baby syndrome)

Do not use water above 10 mg/L nitrate (as nitrogen) for infant formula. Infants cannot adequately reduce methemoglobin; nitrate converts hemoglobin to methemoglobin, which cannot carry oxygen. Cases have been fatal. This risk is acute — a single high-nitrate feeding can cause serious harm.

Chronic adult exposure: colorectal cancer

IARC classifies nitrate in drinking water as a Group 2A probable carcinogen when ingested under conditions promoting endogenous nitrosation. The Iowa Women's Health Study and Danish cohort studies show elevated colorectal cancer risk above 5 mg/L with frequent red meat consumption.

Thyroid disruption

Nitrate competitively inhibits iodide uptake in the thyroid gland. Epidemiological studies associate elevated nitrate exposure with hypothyroidism, particularly in iodine-deficient populations.

The EPA limit: MCL = MCLG = 10 mg/L

Nitrate is one of the few health contaminants where the MCL and MCLG are equal — both set at 10 mg/L (as nitrogen). This is unusual: for most carcinogens the MCLG is zero. EPA concluded 10 mg/L is fully protective against methemoglobinemia. The cancer concern from chronic exposure at lower levels was not fully incorporated into the MCL.

Note: results may be reported as nitrate-nitrogen (NO₃-N) or as total nitrate (NO₃). The MCL of 10 mg/L uses the nitrogen form. If your lab reports total nitrate (not as N), divide by 4.4 to convert.

Testing

Test by colorimetric analysis (EPA Method 353.2) at a certified laboratory. Nitrate test strips can screen for gross contamination but are not accurate enough for health decisions near the 10 mg/L limit. Test annually if you are in an agricultural area, and always after flooding or land use changes nearby.

Find a certified lab and learn how to collect a sample

Treatment

  • Reverse osmosis (RO) — most practical for point-of-use; removes 85–95% of nitrate. Install at the kitchen tap for drinking and cooking water.
  • Ion exchange (nitrate-selective anion resin) — whole-house treatment; specifically designed resins required (standard softener resin is not nitrate-selective).
  • Distillation — effective but slow and energy-intensive.

Note: activated carbon filters and standard water softeners do not remove nitrate.

Compare nitrate treatment systems for private wells

Regulatory framework

MCL: 10 mg/L as nitrogen (N). Also expressed as 45 mg/L as nitrate (NO₃) — these are equivalent.

MCLG: 10 mg/L — equal to the MCL. EPA concluded this level fully protects against methemoglobinemia. The MCL and MCLG being equal is unusual among contaminants with IARC Group 2A classification; chronic carcinogenicity data post-dates the original rulemaking.

Nitrate is regulated under the Phase II Rule (1992). The MCL has not been revised since. A separate MCL of 1 mg/L (as N) applies to nitrite (NO₂⁻).

Detection

EPA Method 353.2 (colorimetric, cadmium reduction). Ion chromatography (EPA Method 300.0) also standard. Detection limits well below 1 mg/L. Nitrate is chemically stable in samples; preserve at 4°C, analyze within 48 hours. No certified lab requirement for private well testing, but certification recommended for accuracy near the MCL.

Geochemistry

Nitrate is highly mobile in oxic groundwater — it does not sorb to aquifer materials and is not naturally attenuated in oxygenated systems. Under reducing conditions (anoxic zones), denitrifying bacteria convert nitrate to N₂ gas (natural attenuation). Deep confined aquifers are thus often nitrate-free. Shallow unconfined aquifers with high recharge rates show direct correlation with land use above the water table.

Data access

USGS NAWQA program and NWIS database contain extensive nitrate well-water records. EPA's ECHO tracks public system compliance. State agricultural agencies often publish watershed-level nitrate data.

Access our data API and methodology

References

  1. Ward, M.H., Jones, R.R., Brender, J.D., et al. (2018). Drinking water nitrate and human health: An updated review. International Journal of Environmental Research and Public Health, 15(7), 1557. https://doi.org/10.3390/ijerph15071557
  2. Schullehner, J., Hansen, B., Thygesen, M., et al. (2018). Nitrate in drinking water and colorectal cancer risk: A nationwide population-based cohort study. International Journal of Cancer, 143(1), 73-79. https://doi.org/10.1002/ijc.31306
  3. Temkin, A., Evans, S., Manidis, T., et al. (2019). Exposure-based assessment and economic valuation of adverse birth outcomes and cancer risk due to nitrate in United States drinking water. Environmental Research, 176, 108442. https://doi.org/10.1016/j.envres.2019.108442