Cited by 183Pharmaceutical and Antibiotic Environmental ImpactsFecal contamination and water qualityWastewater Treatment and Reuse

The DOI matches its Crossref record; 75 of the 81 references it cites were found in a registry or an index; 1 of the 115 sources its claims cite were checked for support.

Septic systems as sources of organic wastewater compounds in domestic drinking water wells in a shallow sand and gravel aquifer

Open access
Schaider, Laurel A., Ackerman, Janet M., Rudel, Ruthann A.·2016·Science of The Total Environment

Abstract

Domestic drinking water wells serve 44 million people in the US and are common globally. They are often located in areas served by onsite wastewater treatment systems, including septic systems, which can be sources of biological and chemical pollutants to groundwater. In this study we tested 20 domestic drinking water wells in a sand and gravel aquifer on Cape Cod, Massachusetts, USA, for 117 organic wastewater compounds (OWCs) and for inorganic markers of septic system impact. We detected 27 OWCs, including 12 pharmaceuticals, five per- and polyfluoroalkyl substances (PFASs), four organophosphate flame retardants, and an artificial sweetener (acesulfame). Maximum concentrations of several PFASs and pharmaceuticals were relatively high compared to public drinking water supplies in the US. The number of detected OWCs and total concentrations of pharmaceuticals and of PFASs were positively correlated with nitrate, boron, and acesulfame and negatively correlated with well depth. These wells were all located in areas served exclusively by onsite wastewater treatment systems, which are likely the main source of the OWCs in these wells, although landfill leachate may also be a source. Our results suggest that current regulations to protect domestic wells from pathogens in septic system discharges do not prevent OWCs from reaching domestic wells, and that nitrate, a commonly measured drinking water contaminant, is a useful screening tool for OWCs in domestic wells. Nitrate concentrations of 1mg/L NO3-N, which are tenfold higher than local background and tenfold lower than the US federal drinking water standard, were associated with wastewater impacts from OWCs in this study.

Overview

AI snapshot

Written from the paper’s full text.

TL;DR

In 20 domestic drinking water wells in a shallow sand and gravel aquifer on Cape Cod, Massachusetts, 85% contained at least one organic wastewater compound, with acesulfame, PFASs, and pharmaceuticals most frequently detected. The authors conclude septic systems are likely the main source, with landfill or commercial wastewater also possible for some PFAS detections.

Key findings

  • Of 117 OWCs analyzed, 27 (23%) were detected in at least one well; 17 of 20 wells (85%) had ≥1 OWC, with a maximum of 13 OWCs in one well. Acesulfame was detected in 17 wells (85%), maximum 5300 ng/L; 12 pharmaceuticals were detected, and 13 wells (65%) had ≥1 pharmaceutical, including sulfamethoxazole in 9 wells (maximum 60 ng/L) and carbamazepine in 5 wells (maximum 62 ng/L).
  • Four PFASs (PFOS, PFHxS, PFBS, PFHxA) were detected in ≥50% of wells, and PFHpA in 30%; maximum concentrations were PFHxS 41 ng/L, PFBS 23 ng/L, PFOS 7 ng/L, and PFHxA 2 ng/L. PFOA was detected in blanks near sample levels; five wells had PFOA at 2–3 ng/L after subtracting the field blank.
  • OWC presence was correlated with nitrate, boron, and acesulfame and inversely correlated with well depth. Wells <15 m had higher median N detects (8 vs. 4 compounds), Σ[pharma] (5.0 vs. 0.4 ng/L), and Σ[PFAS] (6.0 vs. 0.5 ng/L) than deeper wells. Wells with >20 µg/L boron had 3.8 times more detectable OWCs, 7.4 times higher Σ[PFAS], and 8.8 times higher Σ[pharma] than wells with 10–20 µg/L boron.
  • Septic systems were the likely main source, but two wells with the highest Σ[PFAS] (72 and 26 ng/L) departed from the nitrate relationship, suggesting landfill or commercial sources; one well 3.2 km from a capped landfill had the highest acesulfame concentration (5300 ng/L) and PFHxS concentration (47 ng/L).

Methods

  • Recruited 110 volunteer wells, used GIS capture-zone land-use analysis plus nitrate and boron testing to select 20 domestic wells in Barnstable County, Cape Cod, Massachusetts, in areas served exclusively by onsite wastewater treatment systems; raw water samples were collected in February 2011.
  • Analyzed 117 target OWCs using solid-phase extraction with LC-MS/MS for PPCPs, hormones, PFASs, alkylphenols, and herbicides, and large-volume injection GC/MS for organophosphate flame retardants; nitrate was measured by ion chromatography, boron by ICP-MS, sodium by ICP-AES, and total nitrogen and TOC by combustion.
  • Used Spearman rank correlations (p < 0.05) between septic-impact indicators (nitrate, total N, boron, acesulfame, residential density, well depth) and three OWC metrics: total number of OWCs detected, sum of detected pharmaceutical concentrations, and sum of detected PFAS concentrations.

Limitations

  • Stated in the paper: well selection was not designed to be a statistical representation of domestic wells across Cape Cod; capture-zone estimates have considerable uncertainty without site-specific hydrogeological data; TOC correlations could not be tested because TOC was detectable in only five wells; PFOA was detected in laboratory and field blanks at levels close to sample concentrations; alkylphenol method detection limits were relatively high (10–92 ng/L); health-based guideline values were available for only 10 of the 27 detected OWCs, and toxicological data are limited.
  • Evident from the text: the study has a small sample (20 wells), a single sampling event in February 2011, and one region/aquifer, and it lacks isotopic or other source-confirmation analyses, limiting generalizability and causal attribution.

Model-written summary. Check it against the paper before relying on it.

Integrity signals

Registry

Crossref · 10.1016/j.scitotenv.2015.12.081

Cites

75 of 75 references verified0 citation errors · 0 not checkable

Statistics

Nothing to recompute.

Figures

Image 1
CC-BY-NC-ND · From the PDF
Image 2
CC-BY-NC-ND · From the PDF
Image 3
CC-BY-NC-ND · From the PDF
Fig. 1 OWCconcentrations in 20 domestic wells on Cape Cod. Horizontal gray lines show method detection limits. Full chemical names provided in Table 2.
Fig. 1 OWCconcentrations in 20 domestic wells on Cape Cod. Horizontal gray lines show method detection limits. Full chemical names provided in Table 2.CC-BY-NC-ND · From the PDF
Fig. 2 Correlations between pairs of PFASs detected in at least 50% of domestic wells. Dashed gray lines show method detection limits (MDLs). Closed symbols show wells where both PFASs were N MDLs. Open symbols show wells with one or both PFASs b MDL, which were plotted between the MDL and axis as an approximation. For each pair, 6 -8 wells had concentrations b MDL for both PFASs. Concentrations in ng/L.
Fig. 2 Correlations between pairs of PFASs detected in at least 50% of domestic wells. Dashed gray lines show method detection limits (MDLs). Closed symbols show wells where both PFASs were N MDLs. Open symbols show wells with one or both PFASs b MDL, which were plotted between the MDL and axis as an approximation. For each pair, 6 -8 wells had concentrations b MDL for both PFASs. Concentrations in ng/L.CC-BY-NC-ND · From the PDF
Image 6
CC-BY-NC-ND · From the PDF

Verification

Claims the paper makes

77 Not checked yet · 56 Own result · 44 Own interpretation · 7 No basis given · 3 Own method · 1 Partly supported · accuracy not yet measured

Verify all 114 references — free account

Show all 74 claims

  • Probably not a substantial claim. 47
  • It may state two separate claims as one. 86
  • The quote only partly states this claim. 1
114 of 114
  • The paper relies on this without support.

    Eighty-five percent of Cape Cod residents are served by onsite wastewater treatment systems and 20% rely on domestic drinking water wells.

    “Eighty-five percent of Cape Cod residents are served by onsite wastewater treatment systems and 20% rely on domestic drinking water wells.”
  • The paper relies on this without support.

    Incomplete degradation or sorption during treatment in septic tanks and leach fields, as well as leaks of poorly treated sewage from aging and failing systems, allow some organic wastewater compounds to percolate through vadose zone soils and enter groundwater.

    “Incomplete degradation or sorption during treatment in septic tanks and leach fields, as well as leaks of poorly treated sewage from aging and failing systems, allow some OWCs to percolate through vadose zone soils and enter groundwater.”
  • The paper relies on this without support.

    Septic systems may be a source of PFASs in groundwater because household wastewater can contain PFASs that have leached from food packaging, cookware, upholstery, apparel, and other household products.

    “Septic systems may be a source of PFASs in groundwater because household wastewater can contain PFASs that have leached from food packaging, cookware, upholstery, apparel, and other household products.”
  • The paper relies on this without support.

    N detects may include organic wastewater compounds that originate from multiple pollution sources, whereas pharmaceuticals likely originate primarily from household wastewater.

    “N detects may include OWCs that originate from multiple pollution sources, whereas pharmaceuticals likely originate primarily from household wastewater.”
  • The paper relies on this without support.

    Domestic wells are often shallower than large volume public supply wells and thus more vulnerable to contaminants, which often exceed drinking water standards.

    “They are often shallower than large volume public supply wells and thus more vulnerable to contaminants, which often exceed drinking water standards.”
  • The paper relies on this without support.

    Domestic wells are commonly used in communities that are served by onsite wastewater treatment systems (e.g., septic systems, cesspools), which can be sources of pathogens and chemical contaminants to groundwater.

    “Domestic wells are commonly used in communities that are served by onsite wastewater treatment systems (e.g., septic systems, cesspools), which can be sources of pathogens and chemical contaminants to groundwater.”
  • The paper relies on this without support.

    Septic systems and other onsite wastewater treatment systems are the major source of nitrogen to Cape Cod groundwater.

    “Septic systems and other onsite wastewater treatment systems are the major source of nitrogen to Cape Cod groundwater and are the likely source for many of the OWCs that we detected in domestic wells.”
  • The paper relies on this without support.

    Onsite wastewater treatment systems can discharge OWCs into groundwater.

    “All of the sampled wells are located in areas served exclusively by onsite wastewater treatment systems; these systems can discharge OWCs into groundwater.”
  • The paper relies on this without support.

    The OWCs detected in Cape Cod domestic wells are not currently regulated by enforceable drinking water standards.

    “The OWCs we detected in Cape Cod domestic wells are not currently regulated by enforceable drinking water standards and health-based guideline values are only available for 10 of the 27 OWCs we detected.”
  • The paper relies on this without support.

    Local background nitrate concentration is tenfold lower than 1 mg/L NO3-N.

    “We found that nitrate concentrations of 1 mg/L NO 3 -N, which are tenfold higher than local background and tenfold lower than the US federal drinking water standard, were associated with wastewater impacts from OWCs.”
10 of 10

Claims other papers make about this one

Each is checked against this paper’s own text: does it say what the citing paper says it does?

Self-check

Percentages, sums and reported differences re-computed from the paper’s own numbers.

Each contradiction between two passages listed here was confirmed by an independent check.

3 of 3

Citations

Cites

Show all 81 references

Cited by

Sorted by citations

See all 183

Metadata

Authors
Schaider, L. A., Ackerman, J. M., & Rudel, R. A.
Affiliations
Silent Spring Institute (US)
Corresponding author
Schaider, Laurel A.
Venue
Science of The Total Environment
Publisher
Elsevier BV
Published
2016-03
Volume
547
Pages
470-481
ISSN
0048-9697 (ISSN-L)
OpenAlex
W2287549042
Cited by
182
References
81
Citations by year
2026: 16 · 2025: 24 · 2024: 19 · 2023: 13 · 2022: 16 · 2021: 16 · 2020: 19 · 2019: 24 · 2018: 15 · 2017: 14 · 2016: 6
FWCI
10.72
Type
journal article
Language
en
Open access
Locations
  • The Science of The Total Environment (publishedVersion, cc-by-nc-nd)
  • PubMed (publishedVersion)
Funders
  • Massachusetts Environmental Trust
  • Centers for Disease Control and Prevention (1H75EH000732-01)
  • Cape Cod Foundation
Topics
  • Physical Sciences › Environmental Science › Pollution › Pharmaceutical and Antibiotic Environmental Impacts
  • Physical Sciences › Environmental Science › Water Science and Technology › Fecal contamination and water quality
  • Physical Sciences › Environmental Science › Waste Management and Disposal › Wastewater Treatment and Reuse
Keywords
septic systems, groundwater contamination, pharmaceuticals, per- and polyfluoroalkyl substances, organophosphate flame retardants, acesulfame, nitrate, boron, on-site wastewater treatment, sand and gravel aquifers, Cape Cod, landfill leachate, drinking water regulation
MeSH terms
Environmental Monitoring, Massachusetts, Organic Chemicals, Waste Disposal, Fluid, Groundwater, Drinking Water, Water Wells, Wastewater

About these checks

Registry, retraction, Cites and statistics results are computed, not judged, with one exception: a printed reference that no index lists is read once by a model before it counts as a citation error. Claims are extracted by a model and kept only when their quote appears verbatim in the text; each cited source is then checked, with a model’s help, for whether it says what the claim relies on. Those verdicts can be wrong — read the claim’s quote and the cited source before relying on one.

A language model drew the claims from the paper on 2026-10-07, under version 3 of the claim definition (model deepseek-v4.1-flash, prompt extract-v3).

A second model labelled each claim on 2026-10-07 (model jev-1.13-20260917, definition revision gold-guideline-v0.2).

Cited sources are checked with a language model’s help (gpt-6-sol).

Statistics and arithmetic are recomputed, not judged.

Confidence bands are shown only for fields calibrated on our annotated test set. None is calibrated yet, so no band is shown.

What counts as a claim ›How we measure confidence ›How we check this ›

Are you an author, or do you see a problem with this page? Request a review