Glass of water on kitchen bench, PFAS contamination in Australian drinking water

PFAS Contamination in Australian Drinking Water: The 2026 Guide

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PFAS Contamination in Australian Drinking Water: The 2026 Guide

PFAS at a Glance — Australia 2026

ADWG 2025 limit (PFOS+PFHxS combined)8 ng/L
ADWG 2025 limit (PFOA)200 ng/L
Confirmed contamination sites14+ DCCEEW-registered sites across all mainland states and NT
Primary contamination sourceAqueous Film Forming Foam (AFFF) — military airfields and civil aviation training
Best verified removal technologyReverse osmosis: >98%. Activated carbon block: 50–90% variable. Pitcher/gravity filters: inadequate.
Certification to requireNSF/ANSI P473 (specifically written for PFOA + PFOS point-of-use removal)
PFAS half-life in human bodyPFOS ~5 years | PFOA 3–4 years | PFHxS 5–8 years

The contamination report for Williamtown landed in 2016 without warning. Residents near the RAAF base in NSW had been drawing water from bores that testing revealed contained PFAS at concentrations hundreds of times above what Australia would eventually set as a health guideline. Ten years on, the picture is clearer and considerably wider. As a former Royal Australian Navy Clearance Diver, I approach contamination risk the same way I approached water entry in unknown conditions: you assess the hazard, quantify the exposure, and act on data — not assumptions. This guide covers what PFAS are, where Australian contamination is confirmed, what the 2025 ADWG limits mean in practice, and which filter technologies genuinely remove PFAS versus which create the impression of doing so.

What Are PFAS and Why Can’t Your Body Break Them Down?

Per- and polyfluoroalkyl substances are a family of over 12,000 synthetic chemicals built around carbon-fluorine bonds — the strongest bond in organic chemistry. That structural strength is the problem. It is why PFAS do not biodegrade in the environment, why they accumulate in the food chain, and why once they enter the human body they remain there for years. The fluorinated backbone that made PFAS so useful in fire suppression foam, non-stick cookware, and waterproofing compounds is exactly what makes them a persistent exposure risk.

The two compounds most commonly detected in Australian water — PFOS (perfluorooctane sulfonate) and PFOA (perfluorooctanoic acid) — were widely used in Aqueous Film Forming Foam (AFFF), the fire suppression agent deployed at military airfields and civil aviation fire training facilities from the 1970s onward. AFFF contains roughly 1% PFAS by weight. A single large-scale fire training exercise can release hundreds of litres of foam directly onto training ground soil. Over decades of use, the cumulative load on surrounding groundwater and surface water has been substantial at every site where AFFF was used without containment.

PFHxS (perfluorohexane sulfonate) is the third compound now regulated under the ADWG. All three share the same structural persistence. The difference is in their body half-lives: PFOA clears relatively faster (3–4 years), while PFHxS is the most stubborn at 5–8 years. Ongoing exposure — even at low daily levels — means body burden does not return to zero between exposures. The accumulation problem is cumulative and slow-moving in both directions.

Key Takeaway: The “forever chemical” label is not hyperbole. PFOS has an estimated half-life of approximately 5 years in the human body. Stopping exposure does reduce body burden, but it takes years, not weeks. Reducing daily intake from drinking water is the single most actionable lever most households have.

PFAS are not a single substance — they are a class. Short-chain PFAS (fewer than 8 carbon atoms) were introduced as replacements for PFOS and PFOA after 3M voluntarily phased those out in the early 2000s. Short-chain compounds are less bioaccumulative but more mobile in water, travelling further in groundwater plumes from contamination sources. The ADWG currently regulates a specific subset of compounds. The broader class is substantially larger and less well characterised for long-term health effects.

PFAS Contamination Sites Across Australia

The Department of Climate Change, Energy, the Environment and Water (DCCEEW) maintains the national PFAS contamination register. As of 2026, confirmed significant contamination is associated with military and aviation sites in every mainland state and the Northern Territory.

Site State Primary Pathway Status
Williamtown RAAF BaseNSWGroundwater, surface water, bore waterActive management zone
HMAS Albatross (Nowra)NSWGroundwater, Shoalhaven River catchmentActive management zone
Singleton Army BaseNSWGroundwaterUnder investigation
Amberley RAAF BaseQLDGroundwater, Bremer River corridorActive management zone
Oakey Army Aviation CentreQLDGroundwater, bore waterActive management zone
East Sale RAAF BaseVICGroundwater, Latrobe systemActive management zone
Fiskville Fire Training (CFA)VICGroundwater, Moorabool RiverSite decommissioned; contamination managed
RAAF Base PearceWAGroundwater, Swan River catchmentActive management zone
RAAF Base DarwinNTGroundwaterActive management zone
Tindal RAAF Base (Katherine)NTGroundwater, Katherine River — town water affectedFiltration upgrade installed on town supply
RAAF Base EdinburghSAGroundwater, Northern Adelaide PlainsActive management zone

The Katherine case in the Northern Territory is the most significant public health event in the Australian PFAS record. PFAS from Tindal RAAF base contaminated the town water supply to the point where the NT Government provided alternative drinking water to Katherine residents. Testing between 2016 and 2017 found PFOS+PFHxS levels in some sources above the then-applicable health guideline value. A filtration upgrade was subsequently installed on the Katherine town water treatment plant.

The registered sites represent confirmed, documented contamination events with defined management zones. The DCCEEW register does not capture sites currently under preliminary investigation, industrial contamination unrelated to AFFF (chrome plating, semiconductor manufacture, food packaging production), or the growing number of civil airports and fire training sites that also used AFFF historically. The complete national picture is almost certainly larger than what is currently on the register.

Key Takeaway: Contamination plumes do not respect property boundaries. Plumes from high-use sites like Williamtown are measured in kilometres. If you are on bore water or a private tank supply within 10 km of a registered contamination site, you should treat your water source as potentially affected and test independently rather than assume mains-water protections apply to your private supply.

Australian Drinking Water Guidelines 2025: What the Numbers Mean

The National Health and Medical Research Council (NHMRC) sets the Australian Drinking Water Guidelines (ADWG). The 2025 update revised guideline values for the key regulated PFAS compounds. Understanding what these numbers represent — and what they do not — is essential before you can assess your own exposure risk.

Compound ADWG 2025 Guideline US EPA MCL (2024) Basis
PFOS + PFHxS (sum)8 ng/LPFOS: 4 ng/LHealth-based (kidney, thyroid, immune)
PFOA200 ng/L4 ng/LHealth-based (kidney cancer, liver)
PFNANot yet set10 ng/LUnder NHMRC review

The US EPA’s April 2024 maximum contaminant levels are substantially tighter than current Australian guidelines for PFOA (4 ng/L vs 200 ng/L) and slightly tighter for PFOS (4 ng/L vs the 8 ng/L combined PFOS+PFHxS value). This does not mean PFOA is safe at 200 ng/L. It reflects different risk modelling methodologies and the fact that PFOA is excreted somewhat faster than PFOS, reducing its proportional contribution to body burden from chronic low-level exposure. The Australian guideline is the regulatory floor for utilities — “below guideline” does not mean “zero risk”, and the precautionary case for filtering below guideline values remains entirely rational.

Water utilities are required to test for PFAS where contamination is known or suspected. Most capital city water supplies draw from protected catchments without AFFF contamination history and have not detected PFAS above guideline values in routine testing. The risk is concentrated around the registered contamination zones and around private bore water supplies near those zones.

Health Effects of PFAS Exposure: What the Evidence Shows

The health evidence base for PFAS has grown substantially in the decade since Williamtown made national news. Several outcomes now have strong to sufficient evidence bases across multiple study populations.

Immune function suppression. The strongest evidence for harm at environmental exposure levels — below occupational concentrations — is for reduced vaccine antibody response in children. Studies from European cohort data consistently show that children with higher PFAS blood levels mount weaker responses to standard childhood vaccinations. The US National Academies of Sciences 2022 report characterised immune effects as the outcome with the most consistent evidence base for effects at realistic exposure levels.

Thyroid disruption. PFAS compounds — particularly PFHxS — interfere with thyroid hormone transport and binding proteins. Thyroid disruption has downstream consequences for metabolism, cardiac function, and in pregnant women, foetal neurological development. Given PFHxS’s 5–8 year half-life, thyroid-relevant exposure can accumulate significantly in people living near contamination sources over years.

Cholesterol elevation. Elevated total cholesterol and LDL-cholesterol are consistently associated with higher PFAS blood levels across multiple population studies in the US, Europe, and Australia. The mechanism likely involves PFAS interference with bile acid reuptake in the liver, disrupting normal lipid cycling.

Kidney cancer. The International Agency for Research on Cancer (IARC) classified PFOA as a Group 1 carcinogen — known human carcinogen — in 2023, based on sufficient evidence from occupational cohort studies and general population data. The absolute risk increase at environmental versus occupational concentrations remains debated, but the Group 1 classification removes any ambiguity about whether causation is plausible.

Gestational outcomes. PFAS crosses the placental barrier. Higher maternal PFAS exposure is associated with reduced birth weight, earlier gestational age, and altered thyroid hormone levels in cord blood. The PFAS burden in breast milk means exposure begins before birth and continues through the neonatal period, covering a developmental window where thyroid and immune system development is highly sensitive.

Key Takeaway: Pregnant women, households with young children, and anyone near a confirmed contamination site have the strongest precautionary case for active PFAS removal. But the immune suppression and cholesterol data applies broadly enough that filtering below the ADWG guideline — not merely to guideline — is a defensible goal for any household willing to invest in an RO system.

TDS Is Not a PFAS Proxy

A TDS (total dissolved solids) meter is a useful tool for confirming that a reverse osmosis membrane is intact and functioning — but it tells you nothing about PFAS specifically. PFAS are present in water at concentrations in the parts-per-trillion (ng/L) range, far below the detection threshold of any consumer TDS meter. Water measuring 0 ppm TDS can still contain PFAS. Water measuring 3 ppm post-RO — as my Palm Beach tap water measured on a calibrated TDS-3 meter after filtering through a 5-stage RO system — has had significant dissolved solids removed, but the TDS number itself does not confirm PFAS removal to any specific level.

Why this matters: RO is the most effective technology for PFAS removal, and TDS reduction is the most practical proxy available to consumers for confirming the membrane is working. If your RO drops tap water from 69 ppm to 3 ppm, the membrane is clearly functional and rejecting dissolved species at a high rate. A failing membrane that passes dissolved solids will almost certainly also pass PFAS. So TDS is useful as a membrane health indicator — but a working membrane confirmed only by TDS is not the same as a P473-certified result. For definitive PFAS removal verification, the certification matters more than the TDS reading.

PFAS in Bottled Water: Why Switching Is Not the Answer

A common response to PFAS contamination news is switching permanently to bottled water. This is understandable but not necessarily effective, and it is expensive. Australian bottled water is not routinely tested for PFAS under Food Standards Australia New Zealand (FSANZ) regulations. There is currently no mandatory PFAS testing requirement for bottled water in Australia.

US studies have detected PFAS in some bottled water brands — particularly those using municipal tap water sources that are themselves PFAS-affected. The plastic leaching issue from PET bottles adds a separate set of endocrine-disrupting compounds to the exposure picture. And the economics are stark: a household using two litres of bottled water per person per day for a family of four spends approximately $2,400–$4,800 per year. A quality under-sink RO system costs $300–$600 installed, with annual filter changes at $80–$150. The cost comparison resolves clearly in favour of a filter within the first year.

For a detailed analysis of PFAS testing data across Australian bottled water brands, see our guide: PFAS in bottled water Australia — what the data shows.

Which Water Filters Actually Remove PFAS?

Not all filtration technologies are effective against PFAS. The key variables are whether physical rejection or adsorption is the mechanism, contact time with filter media, and whether the filter has been independently certified for PFAS removal. The table below shows performance across common consumer filter types.

Filter Type PFAS Removal Certification Notes
Reverse osmosis (RO)>98% PFOA, PFOSNSF P473, NSF 58Physical membrane rejection. Most consistent, most verified.
Activated carbon block50–90% (variable)NSF 42 or 53 only — no P473Adsorption — degrades with saturation. Not adequate for high-PFAS situations.
Granular activated carbon (GAC)20–60% (inconsistent)NSF 42 onlyChannelling and short contact time. Pitcher and fridge filters use GAC. Inadequate for PFAS.
Gravity filters (Berkey etc.)Unknown — no P473None for PFASProprietary carbon media. No third-party PFAS certification for any gravity filter format.
Pitcher filters (Brita etc.)Negligible to 30%None for PFASBrita explicitly does not certify for PFAS. Contact time is too short.
Ultrafiltration (UF)MinimalNone for PFASUF pore size (0.01–0.1 µm) is orders of magnitude larger than PFAS molecules.

The critical distinction is between RO physical rejection and activated carbon adsorption. RO membranes operate at approximately 0.0001 µm pore size — PFAS molecules at 0.5–2 nm are physically too large to pass through an intact membrane along with dissolved salts. Activated carbon relies on PFAS molecules binding to surface sites, which works but saturates over time and varies with flow rate and water temperature. At low flow rates through a fresh carbon block, PFAS removal can approach 90%. At higher flow rates or after the carbon is partially saturated, the same filter may remove 50% or less.

Key Takeaway: If PFAS removal is your primary goal, reverse osmosis is the only consumer technology with consistently verified performance above 98% and the only format with a standard (NSF P473) written specifically for that purpose. Carbon-only systems — gravity filters, pitcher filters, benchtop carbon units — have no equivalent third-party PFAS certification and variable performance data that does not support relying on them in a confirmed contamination situation.

NSF/ANSI P473: The Certification That Specifically Covers PFAS

NSF International developed the P473 standard to test specifically for PFOA and PFOS removal at point-of-use devices. To achieve P473 certification, a filter must demonstrate it reduces:

  • PFOA from a challenge concentration of 1.5 µg/L to below 0.07 µg/L (95%+ reduction)
  • PFOS from a challenge concentration of 1.5 µg/L to below 0.07 µg/L (95%+ reduction)

This certification is independent — the manufacturer submits the product to NSF or an accredited lab, and the system must maintain that removal throughout its claimed filter life, not just when new. “NSF P473 certified” is a verifiable claim: the NSF product database at nsf.org lists certified products by model number. If a filter product claims P473 but does not appear in the NSF database, the claim is unverified.

For Australian consumers, P473 is the correct certification to require when selecting a point-of-use filter specifically for PFAS. NSF 58 (the broader RO standard) also includes PFOA and PFOS challenge testing within its contaminant reduction claims for certified products. Either certification provides a meaningful performance assurance that manufacturer marketing copy alone cannot.

Recommended RO Systems for PFAS Removal

Given the technology analysis, the only consumer filtration formats with consistent, verified PFAS removal are reverse osmosis systems. The following three options represent the range across installation types and budget points for Australian households.

AquaTru Classic Smart Alkaline — NSF P473 Certified Countertop RO

The AquaTru Classic is the most accessible P473-certified system for Australian households. It requires no plumbing — the unit sits on the bench, connects to your tap, and delivers water through a 4-stage process: sediment pre-filter, reverse osmosis membrane, post-carbon, alkaline filter. The P473 certification covers PFOA and PFOS removal at rated capacity through the membrane’s full service life.

For renters, apartment dwellers, or anyone unwilling to work under a sink, the countertop format removes the installation barrier entirely. The unit produces approximately 1.5 litres per 6-minute cycle at normal tap pressure. For a household filtering drinking and cooking water only, the throughput is adequate. It is not a high-throughput system for whole-household use.

Waterdrop D6 Under-Sink RO — Tankless, High Flow, NSF 58

The Waterdrop D6 is an under-sink tankless RO system certified to NSF/ANSI 58. NSF 58 testing includes PFOA and PFOS challenge testing within its contaminant reduction claims. The D6’s membrane delivers >95% reduction for PFOA and PFOS, consistent with what a 0.0001 µm RO membrane produces when functioning correctly. The tankless design means on-demand delivery without waiting for a storage tank to refill.

The D6 suits homeowners comfortable with a straightforward DIY installation. Once in place it delivers filtered water continuously without cycle-time interruptions. For specification detail and Australian installation notes, see our Waterdrop D6 full review.

EcoHero 5-Stage RO — Under-Sink with Australian Support

Pure Water Systems’ EcoHero 5-Stage is a local option with Australian-based technical support. The 5-stage configuration adds a remineralisation cartridge post-membrane, returning calcium and magnesium to the output water. For PFAS removal, the RO membrane stage delivers equivalent performance to other quality 0.0001 µm membranes. The advantage is local parts availability, AU-based support, and no international freight lead times for replacement filters.

For a full performance assessment, see our EcoHero 5-Stage RO review.

How to Test Your Water for PFAS

PFAS testing requires laboratory analysis. No consumer test kit can detect PFAS at the ng/L concentrations that matter for health assessment. If you live near a known contamination site, on bore water, or want baseline data before making filter decisions, laboratory testing is the correct first step.

Accredited laboratories. In Australia, accredited laboratories offering PFAS panel testing include Eurofins Australia, ALS Environmental, National Measurement Institute (NMI), and the Environmental Analysis Laboratory at Southern Cross University. A targeted 6-compound panel (PFOS, PFOA, PFHxS, PFNA, PFBS, PFHxA) costs approximately $150–$300. A full 24-compound PFAS panel per DCCEEW guidance costs $300–$500 depending on the laboratory and turnaround time.

Sample collection. Use the laboratory-supplied container (typically HDPE, not glass). Run the tap for two minutes before collecting to clear standing water from pipes. Do not use PTFE or Teflon fittings in the collection setup — these components contain PFAS and will contaminate your sample.

Interpreting results. Compare against ADWG 2025 values: 8 ng/L for the sum of PFOS and PFHxS, 200 ng/L for PFOA. Detections below guideline values are not an automatic call to action but they do establish a baseline. If any result exceeds the guideline, contact your state health authority. NSW Health, QLD Health, and WA Department of Health all maintain PFAS-specific response guidance for residents of registered contamination zones.

Decision Framework: Do You Actually Need to Filter for PFAS?

Based on the technology evidence and the Australian contamination geography, here is how I would structure the decision.

You are on mains water in a capital city without a PFAS contamination zone nearby. Your utility-level PFAS risk is low. Most major water supplies have tested clean at the utility level, and your utility annual drinking water quality report will confirm recent testing results. Filtering for PFAS is a reasonable precautionary step — particularly if you have young children or are pregnant — but it is not a response to an immediate documented risk. If you choose to filter for other reasons (chloramine, TDS, taste), an RO system covers PFAS as a co-benefit.

You are near a registered contamination site or on bore water near a military airfield. This is a confirmed problem category, not a theoretical one. NSF P473-certified RO is the appropriate response. The AquaTru Classic is the easiest no-plumbing option for renters. The Waterdrop D6 and EcoHero 5-Stage are the better choices for permanent installation. Test your supply first if you are on bore water — then act on the data.

You are on bore water within 10 km of a military airfield and have never tested. Do not continue using that water as a drinking supply until you have laboratory results. The Williamtown, Oakey, and Katherine cases all demonstrated that people who assumed their bore water was unaffected were wrong. A $200–$300 laboratory test is cheap insurance relative to the alternative.

Final Verdict

For most Australian households on major urban mains water, PFAS is not an immediate documented risk — but the case for precautionary RO filtration is stronger than it was five years ago. PFOA is now a confirmed Group 1 carcinogen. The immune suppression evidence applies at concentrations below the ADWG guideline. If you are going to filter your water for any reason, RO covers PFAS as part of the package and is worth the incremental cost over carbon-only systems.

For households near confirmed contamination sites or on bore water: get a laboratory test, then install an NSF P473 or NSF 58-certified RO system. The filter cost is trivial compared to the documented health consequences of sustained PFAS exposure at contamination-zone concentrations.

Frequently Asked Questions

Does my Sydney or Melbourne tap water contain PFAS?

Sydney Water and Melbourne Water both publish annual drinking water quality reports including PFAS testing results. Neither major supply system has PFAS detections above ADWG guideline values in recent testing. Both utilities source from protected catchments not associated with AFFF use. For most Sydney and Melbourne households on mains water, PFAS is not a documented supply risk. If you want independent confirmation rather than utility data, laboratory testing costs $150–$300 for a targeted PFAS panel.

Does a Brita filter remove PFAS?

No. Brita’s own documentation states that their pitcher filters are not certified or designed to remove PFAS. Standard pitcher filters use granular activated carbon (GAC) with a short contact time — insufficient for reliable PFAS adsorption. If PFAS removal is your goal, you need a reverse osmosis system with NSF P473 or NSF 58 certification. Do not rely on a pitcher filter for PFAS reduction in a known contamination situation.

What is NSF P473 certification and why does it matter?

NSF/ANSI P473 is an independent testing standard specifically written for PFOA and PFOS removal at point-of-use filters. Products certified to P473 have been tested to reduce both compounds from a 1.5 µg/L challenge concentration to below 0.07 µg/L (95%+ reduction) throughout their rated filter life — not just when new. It is verifiable through the NSF product database at nsf.org. It is the most meaningful third-party assurance that a filter actually removes PFAS, rather than being marketed as doing so.

Will boiling water remove PFAS?

No. Boiling water kills pathogens but has no effect on PFAS. Boiling actually concentrates PFAS by reducing water volume while leaving PFAS behind in solution. If you are in a confirmed PFAS contamination area, boiling is not a mitigation strategy and should not be treated as one.

I live near Williamtown RAAF Base — should I be worried about my tap water?

Hunter Water’s mains supply to the Williamtown area has been monitored for PFAS since 2016 and Hunter Water reports that its reticulated mains supply does not contain PFAS above ADWG guideline values. The contamination risk at Williamtown is primarily for bore water users and private water supplies within the DCCEEW-defined investigation area — not for mains water customers. If you are on mains water from Hunter Water, check their annual water quality report for current testing data. If you are on bore water or a private tank supply near the base perimeter, independent laboratory testing is strongly advisable before continuing to use that water for drinking.

Does reverse osmosis remove all PFAS compounds, or only PFOA and PFOS?

RO removes PFAS through physical membrane rejection based on molecular size relative to the membrane pore (~0.0001 µm). Long-chain PFAS including PFOS, PFOA, and PFHxS — the three ADWG-regulated compounds — are reliably rejected at >98%. Short-chain PFAS replacement compounds such as PFBS, GenX, and PFBA are smaller and slightly less well rejected, but removal is still typically >90% in well-functioning RO systems. NSF P473 certification tests specifically for PFOA and PFOS. No current consumer certification standard covers the full spectrum of short-chain PFAS compounds.

How do I find out if my area has PFAS contamination?

The Department of Climate Change, Energy, the Environment and Water (DCCEEW) maintains the national PFAS site register at dcceew.gov.au. Your state health department publishes PFAS-specific guidance for registered sites in your state. For mains water, your utility’s annual drinking water quality report will include PFAS results if the supply has been tested. For bore water or private water supplies, DCCEEW guidance recommends testing if your property is within 10 km of a registered contamination site or downstream of a known plume.

Can PFAS be absorbed through skin when showering?

Dermal absorption during showering is considered a minor exposure pathway for PFAS compared to drinking water ingestion. The relatively large molecular size of PFOS and PFOA limits skin penetration. The primary exposure routes are dietary (including drinking water) and, for contamination zones, soil and dust ingestion. If you are on PFAS-contaminated water, filtering drinking and cooking water is the highest-impact intervention available. Shower filtration specifically for PFAS is not supported by current evidence as a meaningful risk reduction measure.

What are the ADWG 2025 guideline values for PFAS?

The Australian Drinking Water Guidelines 2025 set a combined guideline value of 8 ng/L (nanograms per litre) for the sum of PFOS and PFHxS, and 200 ng/L for PFOA. These are health-based values that water utilities must meet for reticulated mains water. They represent concentrations at which lifetime daily consumption is judged to present an acceptable risk by the NHMRC — they are not zero-harm thresholds, and individuals with higher risk sensitivity may reasonably choose to filter below guideline rather than simply to guideline.

Is activated carbon block filtration adequate for PFAS?

Activated carbon block removes a proportion of PFAS through adsorption — typically 50–90% depending on contact time, flow rate, and filter age. This is substantially better than granular activated carbon in pitcher filters. However, carbon block is not independently certified to NSF P473 standards, its performance degrades as the carbon saturates, and the variability is too high to rely on in a confirmed high-PFAS contamination situation. For low-level background PFAS in areas without documented contamination, a quality carbon block filter may provide adequate precautionary reduction. For households near registered contamination sites, RO is the appropriate choice.

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Jayce Love — Clean and Native founder
Written by Jayce Love

Former Royal Australian Navy Clearance Diver and TAG-E counter-terrorism operator. Founded Clean and Native to apply the same rigorous thinking to the home environment.

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