Full contaminant data, sample history, and sourcing for Bay County. For readers who want to go beyond the summary.
Contaminant Data — All Analytes
79 well testing events on record, covering
19 analytes.
Data spans 1967 to 2024.
Contaminant
Samples
Years
Detection Rate
Distribution LowModHigh
vs. Limit
vs. MI Avg
Chloride
44
1975–1992
98%
352% of limit
↑ 1761% above
Iron
32
1975–1988
100%
207% of limit
↓ 42% below
Sulfate
30
1975–1988
100%
120% of limit
↑ 469% above
Manganese
32
1975–1988
100%
107% of limit
↑ 21% above
Lead
26
1975–1984
23%
2000% of limit
↑ 9748% above
Arsenic
31
1975–1988
81%
20% of limit
↓ 33% below
Fluoride
31
1975–1988
90%
10% of limit
~ typical
HFPO-DA (GenX)
municipal
31
2023–2025
0%
—
—
Nitrate
23
1975–1984
22%
0% of limit
↓ 100% below
Nitrite
23
1975–1984
35%
7% of limit
↑ 490% above
PFHxS
municipal
31
2023–2025
0%
—
—
PFNA
municipal
31
2023–2025
0%
—
—
PFOA
municipal
33
2010–2025
0%
—
—
PFOS
municipal
31
2023–2025
0%
—
—
Uranium
22
1978–1984
23%
2% of limit
↑ 91% above
Hardness
31
1975–1988
100%
—
↑ 125% above
Sodium
31
1975–1988
100%
—
↑ 3085% above
pH
37
1975–1991
100%
—
~ typical
PFBS
municipal
31
2023–2025
0%
—
—
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 MI.
Compare your result with Bay County
Of the 31 arsenic tests on record for Bay County (1975–1988),
19% found none, and half were below 2 µg/L.
Of the 44 chloride tests on record for Bay County (1975–1992),
2% found none, and half were below 825 mg/L.
Of the 31 fluoride tests on record for Bay County (1975–1988),
10% found none, and half were below 300 µg/L.
Of the 32 iron tests on record for Bay County (1975–1988),
0% found none, and half were below 620 µg/L.
Of the 26 lead tests on record for Bay County (1975–1984),
77% found none.
Of the 32 manganese tests on record for Bay County (1975–1988),
0% found none, and half were below 53.5 µg/L.
Of the 23 nitrate tests on record for Bay County (1975–1984),
78% found none.
Of the 30 sulfate tests on record for Bay County (1975–1988),
0% found none, and half were below 300 mg/L.
Of the 22 uranium tests on record for Bay County (1978–1984),
77% found none.
Data Coverage & Gaps
Well-sampled analytes (15+ samples)
Chloride 44 samples
Iron 32 samples
Sulfate 30 samples
Manganese 32 samples
Lead 26 samples
Arsenic 31 samples
Fluoride 31 samples
Nitrate 23 samples
Nitrite 23 samples
PFOA 33 samples
Uranium 22 samples
Hardness 31 samples
Sodium 31 samples
pH 37 samples
Public vs. Private Water in Bay County
29Active public water systems
99,076Residents on public water
5%Households on private wells
Public water systems in Bay 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 Bay 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 Bay 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 Bay County. Census data explorer →
USGS Aquifer Atlas — principal aquifer type underlying Bay 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 Bay County, used in contamination risk scoring. TRI Explorer →
EPA Superfund NPL — National Priorities List sites in or near Bay 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 MI with at least one sample for that analyte.