Plainfield Trash Facts

Water and land

Water, Ash, and the Contamination Record

Plainfield’s public drinking water is drawn from the ground, not from a reservoir. The residues that waste-gasification and incineration plants produce — fly ash, bottom ash and process leachate — are documented in the peer-reviewed literature to carry leachable heavy metals and PFAS, and, in the regulatory record, to have reached groundwater at comparable sites. This page sets those facts side by side, using primary sources.125

Three questions, answered from the record. Where does Plainfield’s water actually come from? How dangerous are the specific contaminants already documented in this kind of ash, on a well-water pathway? And at facilities and processes like the one proposed, what have the ash and leachate done to groundwater elsewhere? Each precedent below is labeled as a comparable precedent, not a prediction, and each is anchored to its primary EPA, CT DEEP, USGS, CDC, IARC or peer-reviewed source.

Part one

Where Plainfield’s Water Comes From

Plainfield does not draw its public supply from a surface reservoir. The relevant water here is groundwater — the same water body under and around the proposed site.

  • The public water system serving Plainfield — Connecticut Water’s Plainfield System, state identifier CT1090081 — draws its supply from groundwater wells, not from a surface-water source.1
  • CT DEEP identifies Connecticut’s stratified-drift deposits, including those of the Quinebaug River basin, as the “most productive aquifers in State… especially where thick, coarse grained, and hydraulically connected to large streams or lakes.” By contrast, the state’s bedrock yields only “adequate supplies for domestic use.” The large-yield water under this region is the stratified-drift aquifer.2
  • The scale of that aquifer is measurable. The State of Connecticut’s own Quinebaug Valley State Trout Hatchery, in Plainfield, draws 1,290,816,000 gallons of groundwater a year from 12 high-volume wells operating around the clock. A 2023 state project to conserve between 632 million and 946 million gallons a year is described by CT DAS and DEEP as “significantly reducing the stress on the aquifer.”3
  • In the rural corridor around the site, homes outside the Connecticut Water service area draw their household supply from private groundwater wells tapping that same subsurface water.12

The aquifer-protection finding, stated plainly. This page does not claim the parcel sits within a state-designated Aquifer Protection Area. CT DEEP’s official Aquifer Protection Areas map for Plainfield and a live point-in-polygon query against DEEP’s own GIS service both return zero regulated Aquifer Protection Area at the site; a 500-meter buffer also returns none, and the nearest APA (Gallup, No. 78) lies roughly 500 to 1,000 meters away. That negative finding is stated here as a fact. The verified water risk is narrower and firmer: Plainfield relies on groundwater — public wells and private wells drawn from the Quinebaug stratified-drift aquifer — and the state trout hatchery draws about 1.29 billion gallons a year from that same aquifer system.2314

Plainfield water supply, from primary sources
MeasureFigureSource
Public supply typeGroundwater wells (system CT1090081)CT Water / CT DPH1
Aquifer typeStratified drift — the state’s most productiveCT DEEP2
Hatchery withdrawal1,290,816,000 gallons per year, 12 wellsCT DAS / DEEP3
Aquifer Protection Area at siteNone — nearest regulated APA ~500–1,000 m awayCT DEEP GIS14

Listed species: what the state map shows, and does not

The proposed site does fall inside a current CT DEEP Natural Diversity Data Base area — a live query against DEEP’s mapped polygons returns a hit at the site (map date June 2026), meaning a state-listed species or a significant natural community is known within the mapped area. But DEEP masks the identity: on all public NDDB products, “exact locations and species names have been masked.” So the accurate statement is this: the site is within a state-mapped listed-species area; the species is not publicly disclosed, and no official record confirms bald eagle specifically. Only a formal DEEP Environmental Review Request could resolve which species is present.1516

Part two

Who Lives Around the Site

Connecticut’s environmental-justice law is not abstract here. Under CGS § 22a-20a, a proposed “affecting facility” in an environmental-justice community must file a meaningful public-participation plan — and CT DEEP already has such a plan on file for the SMART Technology Systems project at Norwich Road and Black Hill Road.45

  • Plainfield is on the state’s 2025 distressed-municipalities list with no grace period, which by statute makes the whole town an environmental-justice community.17
  • The census block groups encompassing the project area are low-income by the state’s own measure: 43.1%, 37.0% and 44.5% of residents live below 200% of the federal poverty level — each above the 30% threshold that defines an EJ community under CGS § 22a-20a(a).17
  • CDC/ATSDR’s Environmental Justice Index places the surrounding census tracts’ environmental burden in the 57th to 75th percentile nationally — a live federal substitute for the EPA EJScreen tool that was removed from public access in February 2025.18

These figures cover the census tracts and block groups encompassing the project area, geocoded from the road-name centroid; no public parcel-boundary service exists to tie them to the exact parcel line. The whole-town distressed / EJ status is firm regardless.

The plant would sit in a state-designated environmental-justice community

Under Connecticut law (CGS 22a-20a), a census block group is an environmental-justice community when 30% or more of residents live below 200% of the federal poverty level. Block groups encompassing the project area:

30% EJ THRESHOLD Tract 9073 (BG1) 43.1% Tract 9073 (BG3) 37.0% Tract 9071 (BG3) 44.5% 0% 50% below 200% FPL

Plainfield is also on the 2025 CT distressed-municipalities list, making the whole town an EJ community. Source: CT DEEP Environmental Justice 2025 Set (block-group data), verified via the state GIS service. portal.ct.gov/deep/environmental-justice

Data
Residents below 200% of the federal poverty level, block groups encompassing the project area
Block groupBelow 200% FPLEJ threshold
Census Tract 9073, BG143.1%30%
Census Tract 9073, BG337.0%30%
Census Tract 9071, BG344.5%30%

Part three

What the Residues Contain — and Why It Matters

Waste-to-energy plants of this kind do not make their input disappear. They convert it into flue gas, energy, and solid and liquid residues — fly ash, bottom ash or slag, and process leachate. What those residues contain is established in the peer-reviewed literature and the federal regulatory record.

  • A 2025 peer-reviewed review in the journal Toxics states that municipal-solid-waste incineration fly ash “is recognized as a hazardous solid waste due to its enrichment in toxic heavy metals and high leaching potential,” naming lead, cadmium, chromium, arsenic, mercury, nickel, copper, zinc and others, alongside chlorides and dioxins. The same review notes that in landfills these pollutants “could migrate through various pathways such as leachate transport, groundwater diffusion, and plant uptake.”25
  • The U.S. EPA has made coal-combustion residuals a formal National Enforcement and Compliance Initiative — “Protecting Communities from Coal Ash Contamination” — citing the “long-term release of contamination into groundwater, drinking water, or surface water.” The heavy metals of concern in coal ash (arsenic, cadmium, chromium, mercury, lead) are the same class found in municipal-waste combustion ash.1125
  • Waste gasification and pyrolysis are regulated as waste incinerators in the United States and the European Union, because the synthetic gas they produce is ultimately combusted; the process is distinct from mass-burn, but the residue and emission concerns are not eliminated by the name.1227

Why those metals matter — and the well-water pathway

The point is not the list of chemical names; it is what authoritative agencies say those specific contaminants do, and that Plainfield’s exposure route is drinking water drawn from the ground.

  • Arsenic and cadmium are classified by IARC as Group 1, carcinogenic to humans. ATSDR ties drinking-water arsenic specifically to bladder, kidney, liver, lung, gastrointestinal, pancreatic and skin cancers, including from in-utero exposure — the exposure route that matters where households draw water from private wells.1924
  • Lead has no known safe blood level. In 2021 the CDC lowered its childhood blood-lead reference value from 5.0 to 3.5 µg/dL and states plainly that no safe level has been identified; low-level exposure lowers children’s IQ, learning and development. Lead is an IARC Group 2A probable carcinogen.2021
  • Mercury and cadmium are governed by federal minimal-risk levels set very low: mercury’s chronic inhalation MRL is 0.3 µg/m³ and its oral inorganic MRL as low as 0.00001 mg/kg/day, while cadmium’s critical effect is kidney (renal tubular) damage. These are the same metals the peer-reviewed review names in the ash, and the reason their leaching potential is treated as a hazard, not a nuisance.222325

PFAS: measured in real facility streams, not destroyed

The concern that thermal treatment does not eliminate PFAS is not an assumption; it has been measured at full-scale plants.

  • At three full-scale waste-incineration plants, PFAS was measured in leachate (mean 215 ng/mL), fly ash (16.4 ng/g) and bottom ash (14.6 ng/g); one plant discharged roughly 384 kg of PFAS a year through leachate alone. PFAS survives combustion and concentrates in the residues.28
  • A 2023 study made the first confirmed measurement of PFAS in waste-to-energy flue gas — 4.0 to 5.6 ng/m³, rising to 27 with sludge co-firing — as well as in bottom ash, air-pollution-control residue and treated process water. PFAS leaves through the stack, not only in ash and water.29
  • A critical review found that PFOA and PFOS only fully mineralize at about 1,000 °C or higher; below that, products of incomplete combustion of unknown toxicity form. Typical municipal-waste plants run below that threshold.30
  • A synthesis of the three disposal routes — landfill, wastewater and incineration — concluded that none eliminates PFAS; each returns it or its breakdown products to another medium, a cyclical problem rather than a destruction solution.31

The residues are not the argument. What the residues have done, in the documented record, is.25

Part four

The Contamination Record

Precedent, not prediction

Each entry below is a documented, comparable precedent — a real facility or process whose groundwater outcome is on the primary regulatory or scientific record. None is offered as a forecast of what the Plainfield proposal would do. Each is offered as evidence of what this class of facility has done, so the risk can be weighed on facts rather than assurances.

In Plainfield: Gallup’s Quarry

Plainfield already has one federally documented groundwater-contamination site — and a gasification plant already operates on part of it.

  • Gallup’s Quarry is a 29-acre former gravel pit in Plainfield placed on the EPA Superfund program after illegal chemical dumping. Groundwater, soil and sediment there carry volatile organic compounds, PCBs and heavy metals; arsenic and 1,4-dioxane were added to monitoring in 2012, and PFAS compounds were detected during the November 2020 groundwater sampling event. The remedy relies on long-term monitoring and institutional controls that restrict use of the contaminated groundwater.6
  • Part of that same Superfund site is now home to the Plainfield Renewable Energy biomass gasification facility, which “became fully operational in January 2014.” Plainfield’s only documented groundwater-contamination site already hosts one gasification plant; the SMART proposal would add a second, larger one taking in mixed municipal waste.7

On Plainfield’s river: the Putnam ash landfill

  • A 2021 CT DEEP adjudication decision documents the Wheelabrator / Waste Innovations ash landfill in Putnam, on the Quinebaug River — the same river system as Plainfield — which receives ash from Connecticut’s trash-to-energy incinerators. Its leachate is sent to the Putnam water pollution control facility, and the decision addresses first-time PFAS testing of that leachate and site groundwater. Ash from a new Plainfield plant would enter the same disposal stream on the same river.8

Coal gasification, decades on: Mason City and Waterloo, Iowa

Two former coal-gasification plants show how long groundwater damage can persist — and that in one case the federal government has declared it beyond cleanup.

  • Mason City, Iowa (operated 1900–1951): coal-tar contamination reached both the shallow and the deeper aquifer. EPA’s April 2023 five-year review found that in the deeper aquifer, “levels of benzene and benzo(a)anthracene were increasing at some locations” — more than seventy years after the plant closed.9
  • Waterloo, Iowa (operated 1901–1956): contamination was severe enough that EPA “determined that it was not feasible to clean up all of the groundwater contamination” and designated a “technical impracticability zone.” The groundwater there “is expected to remain contaminated for the foreseeable future.”10

PFAS from combustion: Norlite, New York

  • At the Norlite incinerator in Cohoes, New York, which burned PFAS-laden firefighting foam under federal contract, Bennington College sampling reported by The Intercept found PFAS in soil and water around the plant, with PFOS measured “twice as high downwind from the facility than upwind of it.” The plant sits less than 200 meters from a public-housing complex home to more than 70 families; New York regulators directed a halt to the foam incineration, and the State subsequently enacted a law banning PFAS-foam incineration in cities including Cohoes. This is an academic sampling result reported in the press, presented here as such; the regulatory action is on the official record.1332

The national pattern: coal ash and groundwater

  • The most comprehensive national analysis of federal coal-ash monitoring data, by the Environmental Integrity Project with Earthjustice, found that 242 of 265 monitored U.S. coal plants — about 91 percent — had unsafe levels of at least one coal-ash pollutant in nearby groundwater, including arsenic, lithium, cobalt and cadmium. The same heavy metals appear in municipal-waste combustion ash.2611

Where coal-ash is stored, the groundwater is usually contaminated

Coal ash carries the same heavy metals (arsenic, mercury, cadmium, chromium) found in municipal-waste incineration and gasification ash. Of U.S. coal plants with monitoring data:

91% contaminated

242 of 265 plants. Source: Environmental Integrity Project & Earthjustice analysis of industry monitoring data required under the EPA Coal Ash Rule (2019). earthjustice.org

Data
U.S. coal plants with public groundwater monitoring data
ResultPlantsShare
Groundwater above a federal limit for a coal-ash pollutant24291%
Not above a federal limit239%
Total monitored265100%
Documented contamination precedents, each anchored to its primary source
Site or datasetWhat the primary record showsPrimary source
Gallup’s Quarry, Plainfield CTVOCs, PCBs, heavy metals, arsenic, 1,4-dioxane; PFAS in Nov 2020 sampling; a gasification plant now operates on part of the siteEPA Superfund67
Wheelabrator ash landfill, Putnam CTAsh landfill on the Quinebaug River; leachate to Putnam WPCF; first-time PFAS testing orderedCT DEEP decision8
Mason City IA gasificationBenzene and benzo(a)anthracene increasing in the deeper aquifer, 2023 reviewEPA Superfund9
Waterloo IA gasificationTechnical Impracticability Zone; groundwater cleanup declared not feasibleEPA Superfund10
Norlite, Cohoes NYPFOS ~2× higher downwind in academic sampling; <200 m from public housing; NY banned PFAS-foam incineration in CohoesNY State; Bennington via press1332
U.S. coal plants (265 sites)~91% with unsafe coal-ash pollutant levels in groundwaterEIP / Earthjustice26

Questions and answers

Frequently Asked Questions

Where does Plainfield get its drinking water?

Plainfield’s public water system (CT1090081) draws from groundwater wells, and homes in the rural corridor outside the service area use private groundwater wells. The relevant water body is the aquifer, not a surface reservoir.12

Is the proposed site on a designated Aquifer Protection Area?

No. CT DEEP’s official Aquifer Protection Areas map and a live GIS query both return zero regulated Aquifer Protection Area at the site; the nearest one is roughly 500 to 1,000 meters away. What is documented is that the region’s water is groundwater from the productive stratified-drift aquifer that supplies wells and the state trout hatchery.142

Is the proposed site in a mapped wildlife-protection area?

It is within a state-mapped listed-species area; the species is not publicly disclosed, and no official record confirms bald eagle specifically. CT DEEP’s Natural Diversity Data Base masks species identity on all public products, and only a formal Environmental Review Request could identify what is present.1516

Are the metals in the ash actually dangerous in drinking water?

Yes, by authoritative classification. Arsenic and cadmium are IARC Group 1 human carcinogens, arsenic in drinking water is tied to several cancers, and lead has no known safe blood level per the CDC. Plainfield’s exposure route is groundwater drawn from wells, which is why the leaching potential of these metals matters here.192024

Does gasification or incineration ash contain contaminants that can reach groundwater?

The peer-reviewed literature classifies municipal-waste incineration fly ash as a hazardous waste “due to its enrichment in toxic heavy metals and high leaching potential,” and notes those pollutants can migrate through leachate and groundwater. EPA treats coal-ash groundwater contamination as a national enforcement priority.2511

Is PFAS destroyed when waste is burned?

Not reliably. PFAS has been measured surviving into leachate, fly ash, bottom ash and even the flue gas of full-scale plants; full mineralization needs about 1,000 °C, above what typical municipal-waste plants reach. No disposal route studied — landfill, wastewater or incineration — eliminates it.2830

Has a gasification plant ever contaminated groundwater beyond repair?

At the former Waterloo, Iowa coal-gasification site, EPA determined full groundwater cleanup was not feasible and designated a “technical impracticability zone” expected to remain contaminated for the foreseeable future.10

Does Plainfield already have a documented contamination site?

Yes. Gallup’s Quarry is an EPA Superfund site in Plainfield where PFAS was detected in November 2020 groundwater sampling; a biomass gasification plant now operates on part of it.67

Sources

Where These Facts Come From

Official & regulatory sources

  1. Connecticut Water Company, Plainfield System Consumer Confidence Report (public water system CT1090081; supply drawn from groundwater wells). ctwater.com (PDF). Corroborated by the U.S. EPA / EWG public-water-system record for CT1090081. ewg.org
  2. Connecticut Department of Energy and Environmental Protection, “Connecticut’s Aquifers” (stratified-drift deposits are the “most productive aquifers in State”; bedrock yields “adequate supplies for domestic use”). portal.ct.gov/DEEP
  3. Connecticut Department of Administrative Services and DEEP, “DAS and DEEP Announce Improvement to Quinebaug Trout Hatchery” (1,290,816,000 gallons of groundwater a year from 12 high-volume wells; conservation of 632,499,840–946,080,000 gallons a year, “significantly reducing the stress on the aquifer”). portal.ct.gov/DAS
  4. CT DEEP, Environmental Justice Public Participation Plan on file for SMART Technology Systems, LLC, Norwich Road / Black Hill Road, Plainfield. portal.ct.gov (PDF)
  5. Connecticut General Statutes § 22a-20a, “Environmental justice community… Meaningful public participation plan… Denial of permit for proposed affecting facility” (a proposed affecting facility in an environmental-justice community must file a public-participation plan in connection with its permit application; a municipality on the distressed list is an environmental-justice community). cga.ct.gov
  6. U.S. EPA, Gallup’s Quarry Superfund site profile, Plainfield CT — cleanup activity (29-acre former gravel pit; VOCs, PCBs, heavy metals; arsenic and 1,4-dioxane added to monitoring in 2012; “PFAS compounds were detected during the November 2020 groundwater sampling event”; long-term monitoring and institutional controls). cumulis.epa.gov
  7. U.S. EPA, Gallup’s Quarry Superfund site profile — redevelopment (“a portion of the site is home to the Plainfield Renewable Energy biomass facility… became fully operational in January 2014”; approximately 37.5 megawatts). cumulis.epa.gov
  8. CT DEEP Office of Adjudications, Wheelabrator Putnam decision (2021) (ash landfill in Putnam on the Quinebaug River receiving ash from Connecticut trash-to-energy incinerators; leachate sent to the Putnam water pollution control facility; first-time PFAS testing of leachate and groundwater). portal.ct.gov (PDF)
  9. U.S. EPA, Mason City Coal Gasification Plant Superfund site profile, Iowa (operated 1900–1951; PAHs, BTEX, coal-tar DNAPLs; April 2023 five-year review found benzene and benzo(a)anthracene increasing at some deeper-aquifer locations). cumulis.epa.gov
  10. U.S. EPA, Waterloo Coal Gasification Plant Superfund site profile, Iowa (operated 1901–1956; coal tar, PAHs, BTEX, cyanide, arsenic, phenols, metals; “not feasible to clean up all of the groundwater contamination,” a designated “technical impracticability zone” “expected to remain contaminated for the foreseeable future”). cumulis.epa.gov
  11. U.S. EPA, “Protecting Communities from Coal Ash Contamination” National Enforcement and Compliance Initiative (coal-ash groundwater contamination as a national enforcement priority; “long-term release of contamination into groundwater, drinking water, or surface water”). epa.gov
  12. U.S. EPA, Advance Notice of Proposed Rulemaking, “Potential Future Regulation Addressing Pyrolysis and Gasification Units” (Sept. 8, 2021) — EPA’s stated position that pyrolysis and gasification units combusting solid waste are “solid waste incineration units” subject to Clean Air Act section 129. Establishes, from the agency record, that these processes are regulated as incinerators in the United States. federalregister.gov. Agency fact sheet: epa.gov (PDF)
  13. Office of the Governor of New York, “Governor Cuomo Signs Legislation Banning Incineration of Firefighting Foam Containing PFAS in Certain New York Cities” (state law prohibiting incineration of AFFF containing PFAS in designated cities, including Cohoes; NY DEC had directed Norlite to cease AFFF incineration, in writing, in June 2020). Establishes the official regulatory action at Norlite. governor.ny.gov
  14. CT DEEP, Aquifer Protection Areas — Plainfield (official town map, April 2026) and the DEEP Aquifer Protection Areas live feature service. A point-in-polygon query at the site’s geocoded coordinates (41.7084, -71.9396) returns zero intersecting Aquifer Protection Area; a 500-meter buffer also returns none; the nearest regulated APA (Gallup, No. 78) is roughly 500 to 1,000 meters away. Plainfield’s four APAs are Gallup (No. 78), Hopeville Road (No. 84), Plainfield (No. 71) and Brooklyn (No. 68); none covers the Norwich Road / Black Hill Road site. Town map: cteco.uconn.edu (PDF). Live service: portal.ct.gov/DEEP
  15. CT DEEP, Natural Diversity Data Base Areas — Plainfield (official town map, map date June 2026) and the DEEP Natural Diversity Database live feature service. A query at the site’s geocoded coordinates returns one NDDB Area polygon (OBJECTID 21875, map date June 2026), meaning a state-listed species or significant natural community is known within the mapped area. portal.ct.gov (PDF)
  16. CT ECO / CT DEEP, Natural Diversity Data Base Areas Resource Guide (DEEP policy that on all public NDDB products “exact locations and species names have been masked,” and that a site-specific species determination requires a formal Environmental Review Request — the only mechanism that could confirm or deny a specific species such as bald eagle). cteco.uconn.edu
  17. CT DEEP, Environmental Justice 2025 Set (block groups and distressed municipalities), via the state ArcGIS / geodata service. Plainfield is on the 2025 distressed-municipalities list with no grace period, making the whole town an environmental-justice community under CGS § 22a-20a(a). Three block groups encompassing the project area exceed the 30% low-income threshold: Census Tract 9073 BG1 (43.1% below 200% of the federal poverty level), Tract 9073 BG3 (37.0%), and Tract 9071 BG3 (44.5%). portal.ct.gov/deep/environmental-justice
  18. CDC/ATSDR, Environmental Justice Index (EJI), 2024 update, via the CDC ArcGIS service. Census Tract 9073 (09015907300) overall EJI 64.5th percentile (environmental burden 64.5th); Tract 9072 (09015907200) overall 58th (environmental burden 75.4th); Tract 9071 (09015907100) overall 42.7th (environmental burden 57th). A live national-percentile substitute for the EPA EJScreen tool removed from public access in February 2025. atsdr.cdc.gov
  19. IARC Monographs Volume 100C, “Arsenic, Metals, Fibres, and Dusts” (2012) — arsenic and cadmium, and their compounds, classified Group 1, carcinogenic to humans. publications.iarc.who.int
  20. CDC, “Update of the Blood Lead Reference Value — United States, 2021,” MMWR (2021) (childhood blood-lead reference value lowered from 5.0 to 3.5 µg/dL; no known safe blood-lead level). doi.org/10.15585/mmwr.mm7043a4
  21. ATSDR, ToxFAQs for Lead (2020) (nervous system is the main target; low-level exposure decreases children’s mental development, learning, IQ and behavior; IARC Group 2A probable carcinogen). atsdr.cdc.gov (PDF)
  22. ATSDR, Toxicological Profile for Mercury — Minimal Risk Levels (2024) (chronic inhalation MRL 0.3 µg/m³, tremors; oral inorganic MRL as low as 0.00001 mg/kg/day, renal effects). ncbi.nlm.nih.gov
  23. ATSDR, Toxicological Profile for Cadmium — Health Effects (2012) (kidney is the primary target; renal tubular dysfunction is the critical effect underlying EPA’s reference dose). ncbi.nlm.nih.gov
  24. ATSDR, Toxicological Profile for Arsenic — Health Effects (2016) (drinking-water arsenic linked to bladder, urothelial, gastrointestinal, kidney, liver, lung, pancreatic and skin cancers, including from in-utero exposure). ncbi.nlm.nih.gov

Scientific & technical studies

  1. Peer-reviewed review, “Recent Advances in Heavy Metal Stabilization and Resource Recovery from Municipal Solid Waste Incineration Fly Ash,” Toxics (2025) (MSWI fly ash “is recognized as a hazardous solid waste due to its enrichment in toxic heavy metals and high leaching potential”; lead, cadmium, chromium, arsenic, mercury and others plus dioxins; migration via “leachate transport, groundwater diffusion, and plant uptake”). ncbi.nlm.nih.gov/pmc
  2. Environmental Integrity Project with Earthjustice, national analysis of federal coal-ash monitoring data (242 of 265 monitored U.S. coal plants — about 91 percent — with unsafe levels of at least one coal-ash pollutant in groundwater, including arsenic, lithium, cobalt and cadmium). earthjustice.org
  3. Global Alliance for Incinerator Alternatives (GAIA), “Waste Gasification and Pyrolysis: High Risk, Low Yield Processes for Waste Management” (in the U.S. and E.U., gasification and pyrolysis are regulated as waste incinerators because the resulting syngas is combusted). no-burn.org
  4. Peer-reviewed measurement study, “Poly- and perfluoroalkyl substances (PFAS) in leachate, fly ash, and bottom ash from waste incineration plants,” Science of the Total Environment (2021) (three full-scale plants: leachate mean 215 ng/mL, range 21.4–682; one plant ~384 kg PFAS/yr via leachate; fly ash 16.4 ng/g, bottom ash 14.6 ng/g; PFAS survives and concentrates in ash and leachate). doi.org/10.1016/j.scitotenv.2021.148468
  5. Peer-reviewed study, “Emission of Per- and Polyfluoroalkyl Substances from a Waste-to-Energy Plant,” Environmental Science & Technology (2023) (first confirmed PFAS in WTE flue gas: 4.0–5.6 ng/m³ normal, up to 27 with sludge co-firing; also in bottom ash, air-pollution-control residue and treated process water; total release 7–20 g/yr, up to 56 with sludge). doi.org/10.1021/acs.est.2c08960
  6. Peer-reviewed critical review, “Thermal Decomposition of Per- and Polyfluoroalkyl Substances,” Environmental Science & Technology (2022) (PFOA/PFOS begin decomposing at 350–450 °C but full mineralization needs at least ~1,000 °C; below that, products of incomplete combustion of unknown toxicity form, and PFAS/PICs are found in combustor ash; typical MSW WTE units run below 1,000 °C). doi.org/10.1021/acs.est.2c02251
  7. Peer-reviewed analysis, Stoiber, Evans & Naidenko, “Disposal of products and materials containing per- and polyfluoroalkyl substances (PFAS): a cyclical problem,” Chemosphere (2020) (none of the three disposal routes — landfill, wastewater, incineration — eliminates PFAS; each returns it or its breakdown products to another medium). doi.org/10.1016/j.chemosphere.2020.127659

News coverage

  1. The Intercept, “Toxic PFAS Chemicals Are Being Burned in a Low-Income Neighborhood” (reporting Bennington College sampling by Prof. David Bond: PFAS in soil and water around the Norlite incinerator in Cohoes, NY, PFOS “twice as high downwind from the facility than upwind of it”; plant less than 200 meters from a public-housing complex home to more than 70 families; New York regulators directed a halt to AFFF incineration). theintercept.com

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