What nitrate numbers tell you before the legal limit of 10 mg/L

NitrateSmart reads nitrate as a record of human impact, and the reading rests on geology: decades of U.S. Geological Survey groundwater studies fixed what a natural nitrate level looks like and where human activity takes over. The lines at 1, 3, 5 and 10 are each someone’s published finding — geology for 1 and 3, health studies for 5, federal law for 10.

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<1 1–3 3–5 5–10 10+
Natural backgroundbelow 1 — consistent with nature
Human impact likelyat 1 — a human fingerprint appears
Human impact clearat 3 — human activity leads
Health-study rangeat 5 — studies report associations
Above the federal limitat 10 — federal law acts

The scale is not arbitrary — the breaks come from groundwater surveys

The scale's two most important lines come straight from the U.S. Geological Survey, which spent decades sampling the nation's groundwater to answer one question: how much nitrate is natural, and how much is us.

That work is what makes a nitrate reading legible. Nitrate turns up in water on its own — soil microbes make it, rain and decaying matter carry it down — so its presence alone proves nothing. What the USGS established is the level at which the natural explanation runs out. Below about 1 mg/L as nitrogen, nitrate is consistent with untouched background[1]. Above about 3, it generally indicates human activity[2].

1 and 3 mg/L: above these, geology alone stops explaining the result

These two lines answer a question of provenance: whose nitrate is this? At 1, the water leaves the range that occurs in nature and begins to carry a human fingerprint. USGS work synthesized by Dubrovsky and colleagues in Circular 1350 places that boundary near 1 mg/L as nitrogen[1]. NitrateSmart calls 1–2.99 Human impact likely.

At 3, the fingerprint is no longer in doubt. Madison and Brunett's USGS review set the convention still used today: nitrate above 3 mg/L as nitrogen generally indicates human activities[2]. “Generally indicates” is not “proves” — the number cannot name the field, feedlot or pipe — but at this level natural background no longer explains it. NitrateSmart calls 3–4.99 Human impact clear. Neither line is a health claim; both are about where the nitrate came from.

The fingerprint is mostly agricultural, and the evidence stops short of naming a source

A nitrate reading tells you human activity reached the water; it does not name the activity. But across the country the answer is not an even split. The U.S. Geological Survey's national assessment found agriculture to be the dominant driver of elevated nitrate in groundwater[1] — mainly fertilizer and animal manure, nitrogen applied to land faster than crops take it up, which leaches down and, because groundwater moves slowly, keeps surfacing for decades.

That is why the map of high-nitrate systems looks like a map of farming. The systems that climb into the human-impacted bands cluster in the Corn Belt and other intensively farmed regions, and they are disproportionately small systems drawing from shallow, recently recharged groundwater — the water most exposed to what happens on the fields above it. Larger systems on surface water or deep, blended sources tend to stay low.

Agriculture is not the only human source. Septic systems and wastewater add nitrate too, and matter locally, especially away from farm country — and no single reading can prove where a system's nitrate came from. But when a public supply reports nitrate well above background, the most likely story, the one the national data keeps telling, is an agricultural one.

What else rides along with farm nitrate

Nitrate is worth reading closely because it rarely travels alone. The chemicals applied to a field leach toward groundwater along the same path, so where farm nitrate has reached the water, other agricultural inputs often have too. When USGS sampled shallow groundwater beneath farmland, it measured nitrate and pesticides in the same wells — and the compounds it found most often were herbicides: atrazine and its breakdown product deethylatrazine, metolachlor, simazine, the ones sprayed on the crops above[10].

Where the nitrate comes from manure rather than fertilizer, the fellow travelers change. It then tends to run with fecal bacteria and the pathogens they signal, along with the salts, veterinary antibiotics and hormones that animal waste carries. This is why an elevated nitrate result has long been a standard reason to test a well for bacteria too.

They do not all move identically — nitrate is unusually mobile and persistent, while phosphorus and some pesticides bind to the soil and pathogens are filtered out over distance. So a high nitrate reading does not prove any particular companion is present; it raises the odds, and marks water worth a closer look. And because most of those companions are tested for rarely, if ever, while nitrate is measured almost everywhere, nitrate ends up being an accessible index of how far agriculture has reached into the water — not just a number about itself.

10 mg/L: the federal limit answers one question, and only one

Ten milligrams per liter is the only nitrate number in wide circulation, and it belongs to the law. It is the enforceable federal Maximum Contaminant Level, adopted by the Public Health Service in 1962[5] and re-promulgated by EPA in 1991[6], set to prevent infant methemoglobinemia — a condition that can keep a baby's blood from carrying enough oxygen. Infants under about six months are the population of greatest concern, and pregnancy is the other circumstance the literature concentrates on[13].

As an enforcement threshold it is sound. As a way to read nitrate it is blunt: one line, near the top of the range, for a single acute condition. Almost every American system sits below it, so “under the limit” drops the whole country into one box and discards the rest of the signal. NitrateSmart reports 10 and above as Above the federal limit and treats it as context — not as the point where nitrate starts to mean something.

5 mg/L: a level that matters when it persists

Between the geological lines and the legal one sits the question neither answers: what is higher nitrate, sustained for years, actually associated with? The evidence that puts a line at 5 mg/L as N comes from Iowa. Two studies, published in 2010 and 2016, followed the same cohort of older Iowa women on public water supplies, both reporting in nitrate as nitrogen.

Women whose supply ran above 5 mg/L as N for more than five years showed higher thyroid cancer, at a relative risk of 2.59[11]. Women whose supply ran above the same 5 mg/L for four years or more showed higher bladder cancer, at a hazard ratio of 1.62[12]. The threshold is the concentration; the years are how long it was drunk.

What makes 5 hold is a pattern that shows up in both. In each study the comparison by concentration alone fell short of significance, while the comparison by years spent above 5 reached it. Two different cancers, two independent analyses, the same result: 5 earns its place as a level that matters when it persists, not as a line crossed on a single sample. That is what the band claims, and it is all it claims.

One distinction the Danish work[3][4] draws sharply, and which holds here too: the risk tracked nitrate in the water, not nitrate from vegetables. They are not the same exposure — the source makes the poison[9].

It is observational evidence: it shows associations, not proof of cause, and the difference for any one person is small. The thyroid finding in particular rests on eight exposed cases and an interval that only just excludes no effect. NitrateSmart draws its health-relevant line at 5 and calls 5–9.99 the Health-study range — the band a simple over-or-under-the-limit map makes invisible.

0.14 mg/L — a line NitrateSmart does not use

One threshold sits far below the rest. Temkin and colleagues proposed 0.14 mg/L as nitrogen[8] as a protective target — about seventy times lower than the legal limit — tied to a modeled one-in-a-million cancer risk and adverse birth outcomes. It marks the level below which even the most cautious risk models stop worrying.

NitrateSmart does not draw a band there. 0.14 sits inside natural background — at that level a human signal cannot be separated from nitrate that was always going to be present. A reading near it is not a finding; it is what untouched water looks like.

Most systems read natural background — the signal is in the tail

NitrateSmart classifies 38,762 community water systems in 47 states, serving 296.9 million people.

Share of the 38,762 systems, by band. Most sit in natural background; the colored tail is the human-impacted range a legal-limit view leaves out.

  • Below 127,600 systems · 203.8 million people
  • 1 to 2.996,408 systems · 56.7 million people
  • 3 to 4.992,574 systems · 18.7 million people
  • 5 to 9.991,998 systems · 16.5 million people
  • 10 and above182 systems · 1.18 million people

Only 182 systems reported a result at or above the federal limit. Below them, roughly eleven times as many reported between 5 and 10, and far more carried at least a human fingerprint. In all, 11,162 systems serving about 93.1 million people read at or above natural background — not a finding of harm, but a measure of how much further human activity reaches than the 182 legal exceedances alone would show.

Two numbers describe the same sample, and quoting the wrong one doubles it

Nitrate is reported two ways — as nitrogen or as nitrate ion — and the same water carries two different numbers depending on which is used. The federal limit is 10 mg/L as nitrogen, or about 44 as nitrate ion; to convert ion to nitrogen, divide by 4.43. Every number on this site is as nitrogen. Miss the conversion and one result can look four times worse in one source than in another.

This is not a footnote. It is why Schullehner and colleagues' 2018 study[7] — the largest study of all, at 2.7 million people — does not anchor the health line: its often-quoted “3.87” is an as-ion figure, about 0.87 as nitrogen. The study is sound; citing its number as though it were as-nitrogen is the error.

Why our number can differ from your utility’s report

The two most common reasons are timing and averaging. A utility’s annual Consumer Confidence Report summarizes the previous calendar year’s compliance sampling — the range detected and how it sat against the limit — and it arrives the following summer. NitrateSmart carries each system’s most recent reported result within a three-year window. Where nitrate moves with season or source — common where supplies blend surface water and groundwater, or where recharge is fast — a year that averaged low can still end on a higher reading, and the two documents will not match.

Neither number is wrong; they describe different things. The report tells you how the year went. The most-recent result tells you where the water sits now — a snapshot, not a distribution, and free to move with the next sample. How the records are made comparable — non-detects, detection limits, unit conversions, multiple samples — is set out in How this is built, and the short version lives in Questions.

The bands describe a water source, not a person’s risk

Read in order, each line answers a different question. Geology sets where human impact begins (1) and becomes clear (3). Health research marks a level that matters when it persists (5). The law draws its own line for its own purpose (10). And the strictest risk model (0.14) sits too low to separate signal from background at all. Each line is someone's published finding, not ours.

What the bands report is how strongly human activity, read through nitrate, has marked a water source — and, at or above 5, that the water has entered the range where health studies report associations. They are not a safety verdict, and they do not claim that any level will harm a particular person. Where an infant or a pregnancy is involved, that judgment belongs with a clinician.

References

  1. Dubrovsky, N.M., and others (2010). Nutrients in the Nation's Streams and Groundwater, 1992–2004. U.S. Geological Survey Circular 1350.
  2. Madison, R.J., and Brunett, J.O. (1985). Overview of the occurrence of nitrate in ground water of the United States. U.S. Geological Survey Water-Supply Paper 2275, p. 93–105.
  3. Bondonno, N.P., and others (2024). Source-specific nitrate intake and all-cause mortality. European Journal of Epidemiology 39(8):925–942. doi:10.1007/s10654-024-01133-5
  4. Bondonno, N.P., and others (2025). Source-specific nitrate intake and incident dementia. Alzheimer's & Dementia 21(12). doi:10.1002/alz.70995
  5. U.S. Public Health Service (1962). Drinking Water Standards.
  6. U.S. Environmental Protection Agency (1991). National Primary Drinking Water Regulations. 56 Federal Register 3526.
  7. Schullehner, J., and others (2018). Nitrate in drinking water and colorectal cancer risk. International Journal of Cancer 143(1):73–79.
  8. Temkin, A., and others (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.
  9. Bowles, E.F., and others (2025). Nitrate: “the source makes the poison.” Critical Reviews in Food Science and Nutrition 65(24):4676–4702. doi:10.1080/10408398.2024.2395488
  10. Gilliom, R.J., and others (2006). The Quality of Our Nation's Waters — Pesticides in the Nation's Streams and Ground Water, 1992–2001. U.S. Geological Survey Circular 1291.
  11. Ward, M.H., and others (2010). Nitrate intake and the risk of thyroid cancer and thyroid disease. Epidemiology 21(3):389–395. Thyroid cancer, more than five years on public supply above 5 mg/L nitrate-N: RR 2.59 (1.09–6.19), 8 exposed cases. Exposure reported as nitrate-N.
  12. Jones, R.R., and others (2016). Nitrate from drinking water and diet and bladder cancer among postmenopausal women in Iowa. Environmental Health Perspectives 124(11):1751–1758. Bladder cancer, four or more years above 5 mg/L NO3-N: HR 1.62 (1.06–2.47), 29 cases. Exposure reported as NO3-N.
  13. Ward, M.H., and others (2018). Drinking water nitrate and human health: an updated review. International Journal of Environmental Research and Public Health 15(7):1557. doi:10.3390/ijerph15071557. The federal limit's basis is infant methemoglobinemia; evidence below the limit reviewed, associations inconsistent.
How the records were made. Where they came from, how they were made comparable, and where the inventory is incomplete — on How this is built.
If your number landed where you want to act on it. Three methods remove nitrate, and the most common responses do not — What removes nitrate.

Where the data comes from

USGS
Nitrate background and geology
peer-reviewed
U.S. EPA
10 mg/L federal limit
regulation
State Programs
Compliance sampling
measured
Iowa health studies
5 mg/L benchmark
observational
NitrateSmart

Nitrate in community water systems, from the utilities’ own compliance reporting.

Results reaching back to July 2023 · current through August 9, 2026.

Data & methods

How this is built
Coverage and gaps

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