Licensed in CT & MA | Established 2001

Connecticut Transfer Act Replacement: A CRE Guide

Connecticut's Transfer Act ended March 1, 2026. Cleanup now follows the discovery of a release, not a sale, making due diligence more important than ever.
Important: This article is a commercial real estate overview, not legal, engineering, environmental, or regulatory advice. Property-specific questions should be reviewed with a Connecticut environmental attorney and a qualified environmental professional. Sources are linked throughout and listed in full at the end.

Key Takeaways

  • Connecticut's Property Transfer Program sunset on March 1, 2026. Transfer Act forms are no longer required for transactions after that date.
  • The replacement is the Release-Based Cleanup Program (RBCP). The trigger moved from the transaction to the discovery of an actual release of contamination.
  • Due diligence still matters. In some deals it matters more, because sampling that finds a release can start a regulatory reporting clock.
  • A Phase I records review is not, by itself, "discovery" of a release. Physical sampling that confirms contamination can be.
  • Releases are sorted into tiers with set fees ($500 to $3,000 at assignment) and cleanup runs to soil and groundwater standards based on land use and risk.
  • Legacy Transfer Act sites stay in the old program until verified, though Public Act 25-54 created a path to transition into the new rules.

Connecticut's environmental cleanup system changed on March 1, 2026. The Property Transfer Act no longer applies to new transactions. In its place is a release-based system focused on identifying, reporting, investigating, and cleaning up actual releases of pollution.

For Connecticut commercial property owners, buyers, sellers, developers, and lenders, this is a major change. The old system was tied to the transfer of certain properties and businesses. The new system is tied primarily to the discovery of a release. That distinction can reduce some of the uncertainty and transaction friction that surrounded the Transfer Act, but it does not eliminate environmental due diligence or the potential cost of addressing contamination. In some situations, investigation may now become even more important, because sampling that identifies a release can start regulatory reporting and cleanup obligations. Here is what changed, what did not, and what Connecticut commercial real estate participants should discuss with their advisors before a transaction moves forward.

The core change in one picture

What starts the state cleanup process: the deal, or the dirt.

BEFORE: Transfer Act Trigger: transfer of an "establishment" Forms, certifying party, filing Investigation tied to the deal Clock starts at the transaction AFTER: Release-Based Cleanup Trigger: discovery of a release Report, characterize, remediate No transfer form required Clock starts at discovery

What Changed on March 1, 2026

Connecticut's Property Transfer Program officially sunset on March 1, 2026. For transactions after that date, Property Transfer Act forms are no longer required. Properties already entered into the Property Transfer Program generally remain subject to it until the required investigation, remediation, and verification are complete, unless an available transition process is used (CT DEEP: Property Transfer Program).

The replacement framework is the Release-Based Cleanup Program. Rather than making the transfer of a qualifying "establishment" the central trigger, the new regulations focus on releases of oil, petroleum, chemicals, hazardous waste, and other regulated substances into Connecticut land or water. DEEP defines a release broadly, as essentially any spilling, leaking, discharging, or disposing of such substances onto the land or waters of the state (CT DEEP: Release-Based Cleanup Program).

The Release-Based Cleanup Regulations were adopted on May 16, 2025 and became effective March 1, 2026. They implement the statutory framework in Connecticut General Statutes Sections 22a-134pp through 22a-134xx (CGS Chapter 445b), and the full regulation text is published through the state's eRegulations portal.

Three broad types of release under the new program
CategoryWhat it covers
Existing releaseHistorical contamination newly discovered after the regulations became effective
Significant existing release (SER)Existing pollution presenting a more immediate risk to people or the environment
Emergent reportable releaseNew spills or releases occurring after the system took effect

These categories come from DEEP's program materials (CT DEEP: Regulation Development).

Transaction-Based vs. Release-Based

Under the former Transfer Act, certain transfers involving qualifying businesses or properties could trigger environmental filing, investigation, and remediation obligations. An environmental process could be activated because a covered transaction occurred, even when the parties were still trying to establish whether actionable contamination was present.

The new system is structured differently. A commercial property sale, lease, refinancing, or business transfer does not automatically create a Transfer Act filing obligation simply because the transaction occurs after March 1, 2026. Instead, obligations generally turn on whether an actual release is discovered, how serious it is, and which party is legally responsible for creating or maintaining it. Connecticut law provides that a person who creates or maintains a release after the effective date must report it when required and remediate it to the applicable standards (CGS Chapter 445b).

Removing a statutory transaction trigger from many deals does not mean buyers can safely stop investigating property conditions.
Old system vs. new system, at a glance
FeatureTransfer Act (before)Release-Based Cleanup (after)
Primary triggerTransfer of a qualifying establishmentDiscovery of an actual release
Forms at saleOne of four Transfer Act forms requiredNo transfer form required
InvestigationTied to the transactionA business decision among the parties
ProfessionalsLicensed Environmental Professionals (LEPs)LEPs plus Permitted Environmental Professionals (PEPs)
TrackingPrior DEEP document systemsREACT online tracker for 2026 and later
Cleanup endpointsRemediation Standard RegulationsRelease-Based Cleanup soil and groundwater standards

Environmental Due Diligence Still Matters

A commercial buyer still needs to understand what it is purchasing. A lender still needs to understand the condition of its collateral. A tenant entering a long-term lease may need to understand whether its operations, construction, excavation, or occupancy could be affected by existing contamination. The new system changes the regulatory framework around these conditions. It does not make the conditions disappear.

What environmental due diligence can surface

  • Former industrial or manufacturing uses; underground storage tanks
  • Petroleum releases; chemical storage or handling
  • Dry-cleaning, auto repair, or fueling activity
  • Contaminated soil or groundwater; vapor intrusion concerns
  • Environmental use restrictions; open cleanup cases
  • Prior Transfer Act filings; conditions affecting future redevelopment

DEEP has also launched the Release, Environmental Assessment, and Cleanup Tracker, known as REACT, to receive reports and track cleanup activity. Records submitted in and after 2026 are generally intended to be available through REACT, while older materials may remain in DEEP's prior document systems (CT DEEP: Environmental Cleanup). That makes a DEEP records review an important part of understanding a site's environmental history.

A Phase I Review Is Not the Same as Discovering a Release

This is one of the most important distinctions in the new system. DEEP states that reviewing historical records showing that a release may have occurred does not, by itself, constitute discovery of a release, and that investigations under the new framework will often be driven by business decisions, such as an owner or buyer hiring an environmental professional to investigate a property (CT DEEP: Regulation Development).

In practical transaction terms, that creates a meaningful gap between identifying a concern and confirming a reportable release.

From concern to reportable release
StepWhat happensReportable release?
Records review (Phase I)History, adjoining uses, databases, visible conditionsGenerally no, by itself
Decision to sampleChoosing to move to invasive testingNot yet
Physical sampling (Phase II)Soil, groundwater, vapor, or building-material testingDepends on results
Analytical resultsLab data documenting contaminationCan be, if it meets the definition

A Phase I Environmental Site Assessment generally reviews records, site history, adjoining uses, regulatory databases, and visible conditions. A Phase II may involve soil, groundwater, soil-vapor, or building-material sampling. The decision to move from records review to invasive testing should be made deliberately. That does not mean a buyer should avoid testing. It means the buyer, seller, attorney, lender, and environmental professional should understand in advance what could happen if sampling confirms a release.

Testing Can Start a Regulatory Clock

Under the Release-Based Cleanup Program, newly discovered historical releases may need to be reported immediately, within 120 days, or within one year, depending on the nature and severity of the condition. DEEP notes that sampling under certain remediation programs can begin the applicable reporting schedule once contamination is identified (CT DEEP: Voluntary Remediation Programs). Emergent spills or urgent conditions may require immediate notification through DEEP's 24-hour spill line, while newly discovered historical releases are generally reported through REACT (CT DEEP: Frequently Asked Questions).

Because sampling can start that clock, several questions should be answered before testing begins, not after contamination is found.

Settle these before samples are collected

  • Who authorized the testing, and who receives the results?
  • Who is responsible for reporting a discovered release?
  • Who pays for additional investigation, and who manages cleanup?
  • Can the buyer terminate? Can the seller require confidentiality?
  • What happens if a reporting obligation continues after the deal terminates?
  • Does the access agreement properly allocate responsibility?
  • Will the lender require additional work before closing?

These belong in the purchase agreement, access agreement, lease, financing documents, and environmental scope of work before samples are collected.

The End of Transfer Act Forms Is Not the End of Liability

It would be a mistake to read the new regulations as saying contamination no longer matters during a sale. The Transfer Act filing trigger has ended for post-March 1, 2026 transactions, but environmental liability, cleanup obligations, contractual risk, lender requirements, and federal law still exist. A buyer may inherit practical problems even when it did not create the underlying contamination.

Problems a buyer can inherit even without causing the contamination
Cost & constructionUse & financingOngoing
Delayed constructionLimits on residential or sensitive usesGroundwater monitoring
Higher excavation and disposal costsReduced financing optionsVapor mitigation
Environmental use restrictionsInsurance exclusionsReporting or compliance requirements
 Tenant concerns; lower resale flexibility 

A lender can also impose environmental conditions that go beyond the minimum required by Connecticut law. The absence of a Transfer Act form is not the same as a clean environmental bill of health.

Cleanup Standards Still Depend on the Property and the Release

The new regulations include standards for soil and groundwater cleanup. How much remediation is required can depend on existing and proposed land use, groundwater classification, the contaminant involved, the depth and location of affected soil, exposure pathways, proximity to drinking-water wells, sensitive receptors, whether the contamination is accessible, and whether an environmental use restriction is used.

Connecticut's cleanup criteria
CriterionPurpose
Direct Exposure Criteria (soil)Protect people from contact with contaminated soil
Pollutant Mobility Criteria (soil)Prevent contaminants in soil from migrating into groundwater
Groundwater Protection CriteriaProtect existing and future drinking-water uses of groundwater
Surface Water Protection CriteriaProtect surface water where a groundwater plume discharges to it
Volatilization CriteriaProtect people from vapors migrating from groundwater into buildings

The two soil criteria and three groundwater criteria are defined by DEEP (CT DEEP: Cleanup Standards). The regulations also provide compliance measures, conditional exemptions, institutional controls, permits by rule, and variances for situations such as inaccessible soil, historically impacted material, and widespread polluted fill (CT DEEP: Compliance Measures). In practice, cleanup does not always require removing every trace of a contaminant. The required remedy may depend on actual risk, land use, site conditions, engineering controls, and recorded restrictions, and that determination should be made by the appropriate professionals, not assumed during negotiations.

Releases Are Assigned to Regulatory Tiers

The new program uses a tiering system to classify releases and set oversight, deadlines, and fees. DEEP lists the following base tier-assignment fees (CT DEEP: Release-Based Cleanup Fees).

Base tier-assignment fees

Charged at the time a release is assigned to a tier. Annual fees may also apply and grow with time in tier.

Tier 1A $3,000 Tier 1B $1,500 Tier 2 $1,000 Tier 3 $500 Reduced or waived fees apply to some residential, nonprofit, and brownfield-funded parties.

Annual fees may also apply and increase based on the number of years since first tier assignment, and reduced or waived fees are available for certain governmental, nonprofit, residential, and brownfield-funded parties, including no tier-assignment fee for an owner-occupied single-family home (CT DEEP: Fees). The practical point for a transaction is that a discovered release is not a single, uniform problem. A limited petroleum condition in one area can have a very different timeline, cost, and regulatory path from a significant groundwater plume moving toward a drinking-water receptor.

What Happens to Properties Already in the Transfer Program?

Properties already subject to the Property Transfer Program do not automatically leave it. DEEP states that unverified Transfer Act sites generally remain in the former program until the property has been investigated, remediated, and verified, using the new release-based cleanup standards as the applicable endpoints. Public Act 25-54 also created a process through which certain sites may transition from the Property Transfer Program into the Release-Based Cleanup Program by submitting a report, prepared by a Licensed Environmental Professional, cataloguing the releases identified at the property (CT DEEP: Property Transfer Program).

Owners of existing Transfer Act sites should determine

  • Whether existing obligations remain open, and whether a verification is complete
  • Whether transition to the new process is available, and whether it would be beneficial
  • Whether deadlines, fees, or cleanup procedures would change
  • How an open case affects a sale, lease, refinance, or redevelopment

The answer will be property-specific.

Potential Benefits for Connecticut Commercial Real Estate

Replacing the Transfer Act may remove a significant obstacle from some transactions. State officials argued the old framework discouraged investment in contaminated and formerly industrial properties because parties faced uncertainty, broad investigation requirements, and transaction-triggered obligations. DEEP and the Department of Economic and Community Development stated that nearly 5,000 properties entered the Transfer Act program since the 1980s, while fewer than half had completed remediation by the time the replacement program was implemented (CT DEEP and DECD Announcement).

Nearly 5,000 properties entered the Transfer Act program since the 1980s. Fewer than half had completed remediation.

Intended benefits (not guaranteed outcomes)

  • Fewer transaction-specific environmental filings
  • More predictable treatment of discovered releases
  • A clearer process for historical contamination
  • Better alignment between cleanup and actual environmental risk
  • Greater flexibility for brownfield redevelopment
  • Fewer properties trapped in long-running Transfer Act processes
  • Improved transparency through REACT

These are intended benefits, not guarantees. Actual deal timing still depends on the site, contaminant, environmental findings, responsible parties, financing, and proposed use.

How the New System Changes Transaction Strategy

The release-based framework may reduce some barriers, but it adds new strategic considerations for every role in a deal.

For sellers

A seller may want to know what investigation a buyer intends to perform before granting site access, including the scope of testing, where samples will be taken, who receives lab results, who makes regulatory notifications, whether the buyer must restore test locations, whether the buyer indemnifies the seller for negligent testing, what happens if a release is discovered and the buyer terminates, and whether the environmental report can be shared with others. A basic access letter may no longer be enough for a property with meaningful environmental history.

For buyers

A buyer should not treat the end of Transfer Act filings as permission to reduce due diligence. Understand historical use, prior investigations, open DEEP matters, existing restrictions, intended future use, whether excavation or redevelopment is planned, whether a lender will require testing, whether a release could be reported during the contingency period, whether the agreement allows enough time to characterize a condition, and whether the price reflects identified risk.

For landlords and tenants

Environmental risk is not limited to sales. A tenant may create a release through its operations; a landlord may already own a property with historical contamination; and construction, trenching, utility work, or interior redevelopment can reveal previously unknown conditions. A commercial lease should clearly address hazardous materials, pre-existing conditions, tenant operations, spill reporting, testing rights, remediation responsibility, indemnification, restoration, surrender obligations, and access for environmental work.

For developers

Developers considering former industrial sites should evaluate environmental conditions before finalizing the site plan and construction budget. A project can be affected by soil management, excavation limits, dewatering, groundwater treatment, vapor mitigation, imported clean fill, off-site disposal, utility routing, building placement, environmental use restrictions, and future residential occupancy standards. Environmental planning should occur alongside zoning, civil engineering, architecture, utilities, and financing.

Five Questions to Ask Before a Connecticut Commercial Property Transaction

Is the property still part of the former Property Transfer Program?

The end of new Transfer Act filings does not close existing cases.

What environmental work has already been completed?

Request prior Phase I and Phase II reports, remediation records, tank records, spill reports, closure letters, verifications, environmental use restrictions, and DEEP correspondence.

Will the proposed investigation involve sampling?

Understand the scope before approving soil, groundwater, vapor, or building-material testing, because results can trigger reporting.

Who is responsible if a release is discovered?

The contract should address reporting, access, investigation, cleanup, cost allocation, termination, confidentiality, and survival of obligations.

Does the intended use change the cleanup analysis?

Industrial, retail, office, residential, childcare, healthcare, and mixed-use projects can present different exposure and redevelopment considerations.

What Commercial Property Owners Should Do Now

Connecticut owners do not necessarily need to launch a full environmental investigation just because the law changed. They should, however, organize the information they already have. A practical first step is to assemble the records that tell a property's environmental story.

Assemble these records

  • Prior environmental reports; Transfer Act forms; DEEP correspondence
  • Tank records; spill reports; waste-disposal records
  • Environmental use restrictions; remediation documentation
  • Tenant hazardous-material records
  • Site plans showing former operations
  • Records of wells, septic systems, drains, and oil-water separators

Owners considering a sale or refinance should review these with their attorney and environmental consultant before the property is marketed or a buyer requests invasive testing. The goal is not to manufacture a problem. It is to understand the property before a transaction puts deadlines, deposits, lender requirements, and negotiations in motion.

The Commercial Real Estate Takeaway

The March 1, 2026 change is significant, but the practical message is straightforward: Connecticut commercial property transactions are no longer automatically governed by the Transfer Act filing system, and actual environmental releases now drive the state cleanup process. That could make some sales and redevelopment projects easier. It also makes planning around environmental investigation more important.

A buyer should not assume that no Transfer Act filing means no environmental risk. A seller should not authorize sampling without understanding the possible consequences. A developer should not separate environmental review from project planning. Good information still matters, and the parties who treat environmental diligence as a routine, deliberate part of every deal will be best positioned under the new rules.

Reminder: This article is a commercial real estate overview, not legal, engineering, environmental, or regulatory advice. Property-specific questions should be reviewed with a Connecticut environmental attorney and a qualified environmental professional.

Buying, Selling, or Redeveloping a Property With Environmental History?

Commercial Connection helps buyers, sellers, landlords, tenants, and developers evaluate commercial real estate across Connecticut, including sites with prior industrial, automotive, petroleum, chemical, or other potentially contaminating use. We help identify the property questions to address before a transaction moves forward and coordinate with your legal, engineering, lending, and environmental team.

Discuss a Property or Site Or call John Famiglietti directly: 203-596-7777

You can also browse current Connecticut commercial listings, review property for sale, or explore commercial land and development sites.

Frequently Asked Questions

Is the Connecticut Transfer Act still in effect?

No. The Property Transfer Program sunset on March 1, 2026. Transfer Act forms are no longer required for transactions after that date. However, properties already in the program generally remain subject to it until investigated, remediated, and verified, unless they use an available transition process.

Do I still need an environmental investigation to sell a property?

The state no longer mandates one simply because a property is being sold. Whether to conduct a Phase I or Phase II assessment is now a business decision among buyer, seller, and lender. Skipping diligence can be risky: if a release is later discovered, reporting and cleanup obligations, and possible tier fees, can fall on the owner.

Does a Phase I count as discovering a release?

Generally not by itself. DEEP indicates that reviewing historical records showing a release may have occurred does not constitute discovery. Physical sampling that produces analytical results documenting contamination meeting the regulatory definition is what can constitute a reportable release, which is why the decision to sample should be made deliberately.

How much are the tier fees?

Base tier-assignment fees are $3,000 for Tier 1A, $1,500 for Tier 1B, $1,000 for Tier 2, and $500 for Tier 3. Annual fees may also apply and grow with time in tier. Reduced or waived fees are available for certain governmental, nonprofit, residential, and brownfield-funded parties, and there is no tier-assignment fee for an owner-occupied single-family home.

What happens to a property already in the Transfer Program?

It stays in the Property Transfer Program until investigated, remediated, and verified, using the new release-based standards as endpoints. Public Act 25-54 created a process to transition certain sites into the Release-Based Cleanup Program by submitting an LEP-prepared report cataloguing the releases at the property. Whether transition helps is property-specific.

Why did Connecticut replace the Transfer Act?

The old system was slow and transaction-triggered. State agencies reported that nearly 5,000 properties entered the program since the 1980s, but fewer than half had completed remediation. The release-based approach aims to focus resources on actual releases, reduce transaction friction, and encourage redevelopment of contaminated and formerly industrial sites.

Sources and Further Reading

Primary Connecticut sources

This article provides general commercial real estate information, not legal, engineering, environmental, tax, or regulatory advice. Regulatory thresholds, definitions, fees, criteria, and timelines are governed by the Release-Based Cleanup Regulations, Connecticut statutes, and DEEP guidance, and may change. Confirm requirements for any specific property with qualified Connecticut environmental attorneys and licensed or permitted environmental professionals. Figures and program details cited here reflect DEEP materials current as of mid-2026 and were sourced from the official pages linked above.

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