Full contaminant data, sample history, and sourcing for Richmond County. For readers who want to go beyond the summary.
Contaminant Data — All Analytes
231 well testing events on record, covering
26 analytes.
Data spans 1946 to 2023.
Contaminant
Samples
Years
Detection Rate
Distribution LowModHigh
vs. Limit
vs. GA Avg
PFOS
municipal
20
2023–2025
20%
656% of limit
↑ 362% above
Iron
187
1955–2023
43%
15% of limit
↓ 63% below
PFHxS
municipal
20
2023–2025
20%
234% of limit
↑ 457% above
PFOA
municipal
20
2023–2025
10%
665% of limit
↑ 385% above
Manganese
179
1967–2023
90%
6% of limit
↓ 90% below
Radon
30
2013–2023
100%
61% of limit
↑ 237% above
Fluoride
180
1946–2023
46%
0% of limit
↓ 95% below
Uranium
10
1999–2019
20%
0% of limit
↓ 28% below
Sulfate
182
1946–2023
98%
0% of limit
↓ 93% below
Nitrate
135
1946–2023
96%
6% of limit
~ typical
Lead
156
1967–2023
80%
2% of limit
~ typical
Sulfate
182
1946–2023
98%
0% of limit
↓ 93% below
Uranium
10
1999–2019
20%
0% of limit
↓ 28% below
PFNA
municipal
20
2023–2025
0%
—
—
Lead
156
1967–2023
80%
2% of limit
~ typical
Nitrate
135
1946–2023
96%
6% of limit
~ typical
Chloride
189
1946–2023
100%
1% of limit
↓ 54% below
Arsenic
155
1970–2023
6%
0% of limit
↓ 92% below
HFPO-DA (GenX)
municipal
20
2023–2025
0%
—
—
Nitrite
124
1970–2023
8%
0% of limit
↓ 80% below
E. coli
1
2013–2019
0%
—
—
Hardness
201
1946–2023
100%
—
↓ 96% below
PFBS
municipal
20
2023–2025
10%
—
↑ 25% above
pH
217
1955–2023
100%
—
↓ 30% below
Sodium
180
1958–2023
100%
—
↓ 74% below
Total Coliform
1
2013–2019
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 GA.
Compare your result with Richmond County
Of the 155 arsenic tests on record for Richmond County (1970–2023),
94% found none.
Of the 189 chloride tests on record for Richmond County (1946–2023),
0% found none, and half were below 2.14 mg/L.
Of the 180 fluoride tests on record for Richmond County (1946–2023),
54% found none.
Of the 187 iron tests on record for Richmond County (1955–2023),
57% found none.
Of the 156 lead tests on record for Richmond County (1967–2023),
20% found none, and half were below 0.169 µg/L.
Of the 179 manganese tests on record for Richmond County (1967–2023),
10% found none, and half were below 2.51 µg/L.
Of the 135 nitrate tests on record for Richmond County (1946–2023),
4% found none, and half were below 575 µg/L.
Of the 182 sulfate tests on record for Richmond County (1946–2023),
2% found none, and half were below 350 µg/L.
Data Coverage & Gaps
Well-sampled analytes (15+ samples)
Iron 187 samples
Manganese 179 samples
Radon 30 samples
Fluoride 180 samples
Sulfate 182 samples
Nitrate 135 samples
Lead 156 samples
Sulfate 182 samples
Lead 156 samples
Nitrate 135 samples
Chloride 189 samples
Arsenic 155 samples
Nitrite 124 samples
Hardness 201 samples
pH 217 samples
Sodium 180 samples
Limited data (<15 samples) — interpret with caution
Uranium 10 samples
Uranium 10 samples
E. coli 1 sample
Total Coliform 1 sample
No private-well PFAS data for Richmond County
We have no private well sampling data for PFAS compounds (PFOA, PFOS, PFNA, and related chemicals) in Richmond County.
PFAS has been detected in local public water systems (UCMR 5 data) — indicated by the "municipal" badge in the table above — but this does not directly indicate private well contamination.
PFAS testing for private wells requires a dedicated lab panel (~$300–$500). If you are near a military base, airport, or industrial site, consider testing proactively. Learn more about PFAS →
Public vs. Private Water in Richmond County
8Active public water systems
213,306Residents on public water
3%Households on private wells
Public water systems in Richmond 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 Richmond 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 Richmond 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 Richmond County. Census data explorer →
USGS Aquifer Atlas — principal aquifer type underlying Richmond 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 Richmond County, used in contamination risk scoring. TRI Explorer →
EPA Superfund NPL — National Priorities List sites in or near Richmond 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 GA with at least one sample for that analyte.