- PWSID
- MA4238000
- State
- Massachusetts
- System type
- community water system (CWS)
- Population served
- 8,805
- City
- Plainville
- Counties
- Norfolk County
- Primary source water
- groundwater under the influence of surface water
- UCMR 5 sampling
- 2023-02-13 to 2023-11-08 · 2 entry point(s) · water types: GU
- Service-area boundary
- authoritative
PFOS 1–3 × its limit highest single result
PFOS 1–3 × its limit worst entry-point average
Open on the Massachusetts map · All Massachusetts systems · All results
These are monitoring results collected under EPA's Fifth Unregulated Contaminant Monitoring Rule (UCMR 5) at entry points, where treated water enters the distribution system; they are not tap-water samples. They are not compliance determinations: compliance with EPA's 2024 PFAS limits is judged on running annual averages of compliance monitoring, required from 2029, so a single UCMR 5 result at or above a limit is not a violation. “< MRL” means the compound was not quantified at EPA's minimum reporting level; it does not mean zero.
Water purchased from
- North Attleboro Water Dept (MA4211000)
Seller's highest results: PFOA 9 ppt · PFOS 8 ppt · HI 0.402 · detected: PFBA;PFBS;PFHpA;PFHxA;PFHxS;PFOA;PFOS;PFPeA - Foxboro Water Department (MA4099000)
Seller's highest results: PFOA 6.3 ppt · PFOS 6.7 ppt · HI 0.002 · detected: PFBS;PFHxA;PFOA;PFOS;PFPeA
Seller results are the seller's own entry-point samples, not measurements of this system's water. This system's own samples (below) may reflect purchased water, its own sources, or both.
Compared with EPA's 2024 values
| Highest single result | Worst entry-point average* | Limit | |
|---|---|---|---|
| PFOA (ppt) | 4.3 | 1.07 | 4 |
| PFOS (ppt) | 5.9 | 5.28 | 4 |
| Hazard Index | 0.009 | 0.007 | 1.0† |
“<MRL” = every result for the compound was below its reporting limit. * Mean of all samples at each entry point with non-detects = 0 (EPA compliance convention; the Hazard Index also uses non-detects = 0); a screening comparison, not a formal running annual average. † Rescission proposed May 2026. PFOA/PFOS MCL 4 ppt (2024 NPDWR, in effect). PFHxS, PFNA, HFPO-DA (10 ppt each) and the Hazard Index (1.0) are 2024 NPDWR values; EPA proposed rescinding them on 18 May 2026 (comment period closed 20 Jul 2026).
Compared with Massachusetts standards
| Highest single result | Worst entry-point average* | Massachusetts | |
|---|---|---|---|
| PFAS6 (sum) (ppt) | 10.2 | 6.35 | 20 |
Sum standards add the listed compounds within each sample (non-detects = 0). State compliance is normally judged on averages over time; these are screening comparisons.
Sampling history
Sampled 2023-02-13 to 2023-11-08 · 2 entry point(s) · water types: GU · 10 sampling visits. PFAS in ppt (ng/L).
| Date | Entry point | Event | PFOA | PFOS | HI | Other detections |
|---|---|---|---|---|---|---|
| 2023-02-13 | LAKE MIRIMICHI WELLS #1,2,3 (GU) | SE1 | <4 | <4 | 0.006 | none |
| 2023-02-13 | WELL 1, 1A,2, 2A, 5 (GU) | SE1 | <4 | 5.5 | 0.002 | none |
| 2023-05-01 | LAKE MIRIMICHI WELLS #1,2,3 (GU) | SE2 | <4 | <4 | 0.007 | none |
| 2023-05-01 | LAKE MIRIMICHI WELLS #1,2,3 (GU) | SE1 | n/a | n/a | n/a | none |
| 2023-05-01 | WELL 1, 1A,2, 2A, 5 (GU) | SE2 | <4 | 4.6 | 0.002 | none |
| 2023-05-01 | WELL 1, 1A,2, 2A, 5 (GU) | SE1 | n/a | n/a | n/a | none |
| 2023-08-09 | LAKE MIRIMICHI WELLS #1,2,3 (GU) | SE3 | <4 | <4 | 0.009 | none |
| 2023-08-09 | WELL 1, 1A,2, 2A, 5 (GU) | SE3 | <4 | 5.1 | 0.002 | none |
| 2023-11-08 | LAKE MIRIMICHI WELLS #1,2,3 (GU) | SE4 | <4 | <4 | 0.006 | PFBA 5 |
| 2023-11-08 | WELL 1, 1A,2, 2A, 5 (GU) | SE4 | 4.3 | 5.9 | 0.002 | none |
“<4” = not detected at the reporting limit shown; “n/a” = not analyzed in that sample. Highlighted = at or above the 4 ppt MCL. HI computed per sample with non-detects as 0. Other detections lists every other quantified compound (lithium in µg/L).
All results by entry point
240 results. Each column is one sampling visit (date and UCMR 5 sample event). A number is a measured concentration; “< 4” = below the minimum reporting level shown; “–” = not analyzed in that visit. PFAS in ppt (ng/L); lithium in µg/L.
LAKE MIRIMICHI WELLS #1,2,3 facility LM123G · sample point 10024 · groundwater under the influence of surface water
| Compound | MRL | 2023-02-13 SE1 | 2023-05-01 SE1 | 2023-05-01 SE2 | 2023-08-09 SE3 | 2023-11-08 SE4 |
|---|---|---|---|---|---|---|
| PFBA | 5 ppt | < 5 | – | < 5 | < 5 | 5 |
| PFBS | 3 ppt | 11.3 | – | 13.7 | 17.6 | 11.7 |
| 11Cl-PF3OUdS | 5 ppt | < 5 | – | < 5 | < 5 | < 5 |
| 4:2 FTS | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| 6:2 FTS | 5 ppt | < 5 | – | < 5 | < 5 | < 5 |
| 8:2 FTS | 5 ppt | < 5 | – | < 5 | < 5 | < 5 |
| 9Cl-PF3ONS | 2 ppt | < 2 | – | < 2 | < 2 | < 2 |
| ADONA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| HFPO-DA | 5 ppt | < 5 | – | < 5 | < 5 | < 5 |
| NEtFOSAA | 5 ppt | – | < 5 | < 5 | < 5 | < 5 |
| NFDHA | 20 ppt | < 20 | – | < 20 | < 20 | < 20 |
| NMeFOSAA | 6 ppt | – | < 6 | < 6 | < 6 | < 6 |
| PFDA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFDoA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFEESA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFHpA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFHpS | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFHxA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFHxS | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFMBA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFMPA | 4 ppt | < 4 | – | < 4 | < 4 | < 4 |
| PFNA | 4 ppt | < 4 | – | < 4 | < 4 | < 4 |
| PFOA | 4 ppt | < 4 | – | < 4 | < 4 | < 4 |
| PFOS | 4 ppt | < 4 | – | < 4 | < 4 | < 4 |
| PFPeA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFPeS | 4 ppt | < 4 | – | < 4 | < 4 | < 4 |
| PFTA | 8 ppt | – | < 8 | < 8 | < 8 | < 8 |
| PFTrDA | 7 ppt | – | < 7 | < 7 | < 7 | < 7 |
| PFUnA | 2 ppt | < 2 | – | < 2 | < 2 | < 2 |
| lithium | 9 µg/L | < 9 | – | < 9 | < 9 | < 9 |
WELL 1, 1A,2, 2A, 5 facility 10125G · sample point 10005 · groundwater under the influence of surface water
| Compound | MRL | 2023-02-13 SE1 | 2023-05-01 SE1 | 2023-05-01 SE2 | 2023-08-09 SE3 | 2023-11-08 SE4 |
|---|---|---|---|---|---|---|
| PFBS | 3 ppt | 4.5 | – | 3.4 | 3 | 4.7 |
| PFOA | 4 ppt | < 4 | – | < 4 | < 4 | 4.3 |
| PFOS | 4 ppt | 5.5 | – | 4.6 | 5.1 | 5.9 |
| 11Cl-PF3OUdS | 5 ppt | < 5 | – | < 5 | < 5 | < 5 |
| 4:2 FTS | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| 6:2 FTS | 5 ppt | < 5 | – | < 5 | < 5 | < 5 |
| 8:2 FTS | 5 ppt | < 5 | – | < 5 | < 5 | < 5 |
| 9Cl-PF3ONS | 2 ppt | < 2 | – | < 2 | < 2 | < 2 |
| ADONA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| HFPO-DA | 5 ppt | < 5 | – | < 5 | < 5 | < 5 |
| NEtFOSAA | 5 ppt | – | < 5 | < 5 | < 5 | < 5 |
| NFDHA | 20 ppt | < 20 | – | < 20 | < 20 | < 20 |
| NMeFOSAA | 6 ppt | – | < 6 | < 6 | < 6 | < 6 |
| PFBA | 5 ppt | < 5 | – | < 5 | < 5 | < 5 |
| PFDA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFDoA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFEESA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFHpA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFHpS | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFHxA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFHxS | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFMBA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFMPA | 4 ppt | < 4 | – | < 4 | < 4 | < 4 |
| PFNA | 4 ppt | < 4 | – | < 4 | < 4 | < 4 |
| PFPeA | 3 ppt | < 3 | – | < 3 | < 3 | < 3 |
| PFPeS | 4 ppt | < 4 | – | < 4 | < 4 | < 4 |
| PFTA | 8 ppt | – | < 8 | < 8 | < 8 | < 8 |
| PFTrDA | 7 ppt | – | < 7 | < 7 | < 7 | < 7 |
| PFUnA | 2 ppt | < 2 | – | < 2 | < 2 | < 2 |
| lithium | 9 µg/L | < 9 | – | < 9 | < 9 | < 9 |
Statistics by compound
| Compound | Results | Detected | Highest (date) | Mean bounds | KM median | P75 | P90 | P95 |
|---|---|---|---|---|---|---|---|---|
| PFBS | 8 | 100% | 17.6 2023-08-09 | 8.74–8.74 | 4.7 | 11.7 | 17.6 | 17.6 |
| PFOS | 8 | 50% | 5.9 2023-11-08 | 2.64–4.64 | <MRL | 5.1 | 5.9 | 5.9 |
| PFBA | 8 | 12% | 5 2023-11-08 | 0.62–5 | <MRL | <MRL | 5 | 5 |
| PFOA | 8 | 12% | 4.3 2023-11-08 | 0.54–4.04 | <MRL | <MRL | 4.3 | 4.3 |
Never detected (26): 11Cl-PF3OUdS, 4:2 FTS, 6:2 FTS, 8:2 FTS, 9Cl-PF3ONS, ADONA, HFPO-DA, NEtFOSAA, NFDHA, NMeFOSAA, PFDA, PFDoA, PFEESA, PFHpA, PFHpS, PFHxA, PFHxS, PFMBA, PFMPA, PFNA, PFPeA, PFPeS, PFTA, PFTrDA, PFUnA, lithium.
Left-censored Kaplan–Meier statistics (Helsel 2005; Helsel & Lee 2006, NADA for R). Units: ppt; lithium µg/L. Each compound has one reporting limit, so the Kaplan–Meier mean equals the upper mean bound (non-detects at the MRL); the lower bound sets non-detects to 0. “<MRL” = the percentile falls below the reporting limit and cannot be estimated. These describe this system's UCMR 5 samples, not population estimates.
Sources
- EPA UCMR 5 occurrence data text files (UCMR5_All.txt; samples 2023-01-09 to 2026-05-28; data summary dated Jul 2026)
- EPA SDWIS via ECHO SDWA downloads, quarter 2026Q3
- EPA Public Water System Service Areas v3 (Mar 2026)
- US Census Bureau cartographic boundary counties 1:500k, 2024
- EPA/USGS NHDPlus V2 (medium resolution) flowlines, Strahler order 2+
Data build a6eeb89a233e · 2026-10-18T04:09Z · UCMR 5 release Jul2026 · SDWIS 2026Q3. Data and methods.