Full contaminant data, sample history, and sourcing for Langlade County. For readers who want to go beyond the summary.
Contaminant Data — All Analytes
90 well testing events on record, covering
20 analytes.
Data spans 1967 to 2025.
Contaminant
Samples
Years
Detection Rate
Distribution LowModHigh
vs. Limit
vs. WI Avg
Manganese
82
1970–2023
60%
80% of limit
↓ 41% below
Iron
82
1970–2023
61%
17% of limit
↓ 93% below
PFOS
municipal
10
2022–2025
20%
113% of limit
↑ 91% above
Nitrate
76
1970–2014
71%
29% of limit
↑ 72% above
Arsenic
26
1976–2023
96%
10% of limit
↓ 35% below
Chloride
82
1970–2023
100%
1% of limit
↓ 73% below
Fluoride
81
1970–2023
85%
5% of limit
~ typical
HFPO-DA (GenX)
municipal
10
2022–2025
0%
—
—
Lead
26
1976–2023
31%
0% of limit
↓ 51% below
Nitrite
70
1975–2014
14%
4% of limit
↑ 265% above
PFHxS
municipal
10
2022–2025
30%
29% of limit
↑ 110% above
PFNA
municipal
10
2022–2025
10%
1% of limit
↓ 53% below
PFOA
municipal
10
2022–2025
30%
46% of limit
↑ 205% above
Radon
1
2003
100%
8% of limit
↓ 52% below
Sulfate
82
1970–2023
93%
3% of limit
↓ 61% below
Uranium
15
1994–2023
100%
5% of limit
↑ 118% above
Hardness
82
1970–2023
100%
—
↓ 34% below
PFBS
municipal
10
2022–2025
30%
—
~ typical
pH
83
1970–2023
100%
—
~ typical
Sodium
82
1970–2023
100%
—
↓ 65% below
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 WI.
Compare your result with Langlade County
Of the 26 arsenic tests on record for Langlade County (1976–2023),
4% found none, and half were below 0.7 µg/L.
Of the 82 chloride tests on record for Langlade County (1970–2023),
0% found none, and half were below 3.1 mg/L.
Of the 81 fluoride tests on record for Langlade County (1970–2023),
15% found none, and half were below 150 µg/L.
Of the 82 iron tests on record for Langlade County (1970–2023),
39% found none, and half were below 9.25 µg/L.
Of the 26 lead tests on record for Langlade County (1976–2023),
69% found none.
Of the 82 manganese tests on record for Langlade County (1970–2023),
40% found none, and half were below 1.38 µg/L.
Of the 76 nitrate tests on record for Langlade County (1970–2014),
29% found none, and half were below 460 µg/L.
Of the 82 sulfate tests on record for Langlade County (1970–2023),
7% found none, and half were below 6.5 mg/L.
Data Coverage & Gaps
Well-sampled analytes (15+ samples)
Manganese 82 samples
Iron 82 samples
Nitrate 76 samples
Arsenic 26 samples
Chloride 82 samples
Fluoride 81 samples
Lead 26 samples
Nitrite 70 samples
Sulfate 82 samples
Uranium 15 samples
Hardness 82 samples
pH 83 samples
Sodium 82 samples
Limited data (<15 samples) — interpret with caution
PFOS 10 samples
HFPO-DA (GenX) 10 samples
PFHxS 10 samples
PFNA 10 samples
PFOA 10 samples
Radon 1 sample
PFBS 10 samples
CDC Health Outcome Correlations
Where contaminants detected in Langlade 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 Langlade 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 Langlade County. Census data explorer →
USGS Aquifer Atlas — principal aquifer type underlying Langlade 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 Langlade County, used in contamination risk scoring. TRI Explorer →
EPA Superfund NPL — National Priorities List sites in or near Langlade 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 WI with at least one sample for that analyte.