Full contaminant data, sample history, and sourcing for Le Sueur County. For readers who want to go beyond the summary.
Contaminant Data — All Analytes
58 well testing events on record, covering
19 analytes.
Data spans 1955 to 2022.
Contaminant
Samples
Years
Detection Rate
Distribution LowModHigh
vs. Limit
vs. MN Avg
PFOA
municipal
21
2023–2025
62%
950% of limit
↑ 121% above
Iron
35
1960–2005
71%
403% of limit
↓ 44% below
Manganese
34
1960–2000
76%
182% of limit
↓ 63% below
PFOS
municipal
18
2023–2025
56%
412% of limit
↑ 105% above
PFHxS
municipal
15
2023–2025
47%
190% of limit
↑ 138% above
Nitrate
39
1960–2005
87%
10% of limit
↓ 59% below
Arsenic
26
1980–2000
46%
46% of limit
↓ 46% below
Chloride
38
1960–2005
100%
1% of limit
↓ 92% below
Fluoride
37
1960–2000
95%
8% of limit
~ typical
HFPO-DA (GenX)
municipal
8
2023–2025
0%
—
—
Lead
26
1980–2000
8%
4% of limit
↓ 90% below
Nitrite
19
1980–2000
11%
4% of limit
↑ 232% above
PFNA
municipal
8
2023–2025
0%
—
—
Sulfate
37
1960–2000
100%
4% of limit
↓ 79% below
Uranium
12
1980–2000
100%
7% of limit
↑ 70% above
Sodium
34
1960–2000
100%
—
↓ 32% below
pH
33
1960–2000
100%
—
~ typical
PFBS
municipal
17
2023–2025
53%
—
↑ 50% above
Hardness
19
1960–2000
100%
—
~ typical
Distribution shows the share of samples in each concentration band relative to the EPA Maximum Contaminant Level (MCL): Low = below half the MCL, Moderate = between half and the MCL, High = above the MCL. Analytes without an MCL (e.g. sodium, pH) show — in the limit columns. State average is based on county median values across MN.
Compare your result with Le Sueur County
Of the 26 arsenic tests on record for Le Sueur County (1980–2000),
54% found none.
Of the 38 chloride tests on record for Le Sueur County (1960–2005),
0% found none, and half were below 1.46 mg/L.
Of the 37 fluoride tests on record for Le Sueur County (1960–2000),
5% found none, and half were below 300 µg/L.
Of the 35 iron tests on record for Le Sueur County (1960–2005),
29% found none, and half were below 484 µg/L.
Of the 26 lead tests on record for Le Sueur County (1980–2000),
92% found none.
Of the 34 manganese tests on record for Le Sueur County (1960–2000),
24% found none, and half were below 36.5 µg/L.
Of the 39 nitrate tests on record for Le Sueur County (1960–2005),
13% found none, and half were below 290 µg/L.
Of the 37 sulfate tests on record for Le Sueur County (1960–2000),
0% found none, and half were below 10 mg/L.
Data Coverage & Gaps
Well-sampled analytes (15+ samples)
PFOA 21 samples
Iron 35 samples
Manganese 34 samples
PFOS 18 samples
PFHxS 15 samples
Nitrate 39 samples
Arsenic 26 samples
Chloride 38 samples
Fluoride 37 samples
Lead 26 samples
Nitrite 19 samples
Sulfate 37 samples
Sodium 34 samples
pH 33 samples
PFBS 17 samples
Hardness 19 samples
Limited data (<15 samples) — interpret with caution
Uranium 12 samples
Public vs. Private Water in Le Sueur County
50Active public water systems
28,355Residents on public water
40%Households on private wells
Public water systems in Le Sueur County are regulated by the EPA and must test and report contaminant levels. Private well owners are responsible for their own testing — there is no routine monitoring of private wells by any government agency.
CDC Health Outcome Correlations
Where contaminants detected in Le Sueur County have established associations with specific health outcomes, we cross-reference CDC PLACES county-level prevalence data. This is a contextual signal, not a causal claim.
This report aggregates data from the following public databases:
Water Quality Portal (WQP) — groundwater sample results for Le Sueur County from EPA, USGS, and state agencies. Browse WQP data →
EPA Safe Drinking Water Information System (SDWIS) — public water system inventory used to estimate the share of residents on private wells. Browse SDWIS →
Census ACS 5-Year Estimates — well and cistern household counts (variable DP04_0074E) used to calculate the private-well percentage for Le Sueur County. Census data explorer →
USGS Aquifer Atlas — principal aquifer type underlying Le Sueur County, which informs which contaminants are geologically likely. USGS Aquifer Atlas →
EPA UCMR 5 (2023–2025) — PFAS occurrence data from public water systems, used as a proxy indicator for aquifer PFAS exposure. Rows marked "municipal" in the table above come from this source. About UCMR 5 →
EPA Toxics Release Inventory (TRI) — industrial facility chemical releases near Le Sueur County, used in contamination risk scoring. TRI Explorer →
EPA Superfund NPL — National Priorities List sites in or near Le Sueur County, used in contamination risk scoring. Superfund site search →
CDC PLACES — county-level health outcome prevalence (kidney disease, cancer, heart disease) correlated with detected contaminants. About CDC PLACES →
Methodology
Raw records are downloaded from the Water Quality Portal and normalized to µg/L (ppb). Records are deduplicated by sample ID and date, and certified outliers are excluded. Analyte names are mapped to EPA canonical forms. Detection rates, distribution bands, and MCL comparisons are computed from the normalized dataset.
Distribution bands use the EPA Maximum Contaminant Level as the threshold: concentrations below 50% of the MCL are classed as Low, between 50% and 100% as Moderate, and above 100% as High. For analytes without an MCL (sodium, hardness, pH), distribution is not computed.
State comparison uses the median of county median values across all counties in MN with at least one sample for that analyte.