Full contaminant data, sample history, and sourcing for Watonwan County. For readers who want to go beyond the summary.
Contaminant Data — All Analytes
69 well testing events on record, covering
19 analytes.
Data spans 1964 to 2024.
Contaminant
Samples
Years
Detection Rate
Distribution LowModHigh
vs. Limit
vs. MN Avg
Iron
35
1964–2016
97%
1052% of limit
↑ 47% above
Manganese
25
1964–1993
100%
460% of limit
~ typical
PFOS
municipal
8
2023
75%
200% of limit
~ typical
Sulfate
39
1964–2016
100%
78% of limit
↑ 312% above
PFOA
municipal
6
2023
67%
3856% of limit
↑ 797% above
PFHxS
municipal
4
2023
50%
255% of limit
↑ 219% above
Arsenic
24
1980–2009
88%
51% of limit
↓ 41% below
Lead
24
1980–2009
71%
60% of limit
↑ 35% above
Nitrate
35
1964–2009
86%
0% of limit
↓ 98% below
Chloride
56
1964–2025
100%
3% of limit
↓ 60% below
Fluoride
33
1964–2009
97%
7% of limit
~ typical
HFPO-DA (GenX)
municipal
2
2023
0%
—
—
Nitrite
14
1980–2009
14%
1% of limit
↓ 57% below
PFNA
municipal
3
2023
33%
20% of limit
~ typical
Uranium
1
1980
0%
—
—
Hardness
17
1964–1981
100%
—
↑ 116% above
PFBS
municipal
4
2023
50%
—
↑ 31% above
pH
19
1964–1994
100%
—
~ typical
Sodium
35
1964–2016
100%
—
↑ 35% above
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 Watonwan County
Of the 24 arsenic tests on record for Watonwan County (1980–2009),
12% found none, and half were below 2.13 µg/L.
Of the 56 chloride tests on record for Watonwan County (1964–2025),
0% found none, and half were below 7.7 mg/L.
Of the 33 fluoride tests on record for Watonwan County (1964–2009),
3% found none, and half were below 290 µg/L.
Of the 35 iron tests on record for Watonwan County (1964–2016),
3% found none, and half were below 3.13 mg/L.
Of the 24 lead tests on record for Watonwan County (1980–2009),
29% found none, and half were below 3.46 µg/L.
Of the 25 manganese tests on record for Watonwan County (1964–1993),
0% found none, and half were below 230 µg/L.
Of the 35 nitrate tests on record for Watonwan County (1964–2009),
14% found none, and half were below 40 µg/L.
Of the 39 sulfate tests on record for Watonwan County (1964–2016),
0% found none, and half were below 195 mg/L.
Data Coverage & Gaps
Well-sampled analytes (15+ samples)
Iron 35 samples
Manganese 25 samples
Sulfate 39 samples
Arsenic 24 samples
Lead 24 samples
Nitrate 35 samples
Chloride 56 samples
Fluoride 33 samples
Hardness 17 samples
pH 19 samples
Sodium 35 samples
Limited data (<15 samples) — interpret with caution
PFOS 8 samples
PFOA 6 samples
PFHxS 4 samples
Nitrite 14 samples
PFNA 3 samples
Uranium 1 sample
PFBS 4 samples
Public vs. Private Water in Watonwan County
13Active public water systems
8,836Residents on public water
17%Households on private wells
Public water systems in Watonwan 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 Watonwan 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 Watonwan 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 Watonwan County. Census data explorer →
USGS Aquifer Atlas — principal aquifer type underlying Watonwan 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 Watonwan County, used in contamination risk scoring. TRI Explorer →
EPA Superfund NPL — National Priorities List sites in or near Watonwan 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.