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Marine Fisheries Habitat Protection Act: reefing offshore platforms

Authorizes Reefing in Place of inactive offshore structures with a structured, state-linked framework and safety safeguards.

The Brief

The Marine Fisheries Habitat Protection Act authorizes converting certain inactive offshore oil and gas platforms and pipelines into artificial reefs to bolster fish habitat and recreational fishing opportunities, using amendments to the National Fishing Enhancement Act and related provisions. It defines key terms and creates a formal pathway called Reefing in Place for decommissioned structures, supported by a structured process and oversight.

The bill also introduces a framework for state programs to assume liability and fund reefing activities, while preserving existing regulatory regimes and allowing continued traditional decommissioning or alternative reefing options.

At a Glance

What It Does

The bill uses the National Fishing Enhancement Act of 1984 as the framework to convert Inactive Structures into Artificial Reefs, including definitions for Reefing in Place, Eligible Structures, and related terms. It establishes a stepwise process—Notice of Intent, assessments, eligibility determinations, Reef Planning Area designation, and formal approval—before reefing can proceed.

Who It Affects

Directly affected are offshore lessees and operators ofInactive Structures, State Reef Programs, Federal agencies (Interior, NOAA), and coastal communities relying on fisheries and reef-driven tourism.

Why It Matters

It creates a pathway to improve habitat for fish and recreational opportunities while clarifying responsibilities, funding options, and oversight for reefing activities, potentially reducing decommissioning costs and guiding decisions within a national reefing framework.

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What This Bill Actually Does

The bill aims to turn certain inactive offshore oil and gas platforms and pipelines into artificial reefs to boost habitat for fish and support fishing and related coastal economies. It grounds the reefing effort in the National Fishing Enhancement Act of 1984 and introduces a precise vocabulary to avoid ambiguity, including terms like Inactive Structure, Eligible Structure, Reef in Place, and Reef Planning Area.

This vocabulary is used throughout the process to ensure consistent implementation and oversight.

The core mechanism is a formal, time-bound process for reefing. An Applicant (typically a lessee or operator) submits a Notice of Intent to Reef.

Within 180 days, the Director (in collaboration with the Administrator) must oversee an assessment of each Inactive Structure’s habitat value and the economics of reefing versus removing or replacing the structure. If there is an Established Reef Ecosystem nearby or the potential for one, the Director, after review, can determine that the structure is Eligible for Reefing in Place.Once eligible, a Reef Planning Area footprint is designated to guide where reefing could occur, with the caveat that this designation does not automatically convert every nearby structure.

Approval to Reef in Place must occur within three years of eligibility and requires conditions such as permanent wells being plugged, hazardous liquids removed, navigational markers installed if needed, and liability transferred to a State if a State Program is chosen. An annual reporting requirement then tracks all reefing actions and outcomes.

The bill also preserves existing reefing options under other programs and does not preempt pipeline regulatory processes unless designated for an Artificial Reef.

The Five Things You Need to Know

1

The bill creates Reefing in Place as a formal mechanism for Inactive Structures under the National Fishing Enhancement Act.

2

It establishes a stepwise process: Notice of Intent, assessments, eligibility, Reef Planning Area, and approval.

3

Eligibility depends on an Established Reef Ecosystem nearby or potential for one and compliance with plan criteria.

4

States may assume liability and partially fund reefing up to 50% of cost savings, subject to agreement and approval.

5

Removal orders are restricted during key periods to protect reefing timelines and processes.

Section-by-Section Breakdown

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Section 2

Use of offshore platforms and pipelines for artificial reefs—definitions and framework

Section 2 rewrites and expands the definitions in the National Fishing Enhancement Act to create a formal Reefing in Place framework. It defines key terms (Administrator, Artificial Reef, Eligible Structure, Inactive Structure, Reef in Place, Reef Planning Area, State Program, etc.) and anchors the process to assess, designate, and approve reefing actions. The section positions reefing as an explicit option within Covered Waters and ties it to decommissioning outcomes, ensuring a consistent baseline for future reefing decisions.

Section 207

Reef in Place process—Notice, assessment, eligibility, and planning

Section 207 lays out the procedural steps. An Applicant submits a Notice of Intent to Reef; the Director must oversee or appoint an assessment within 180 days, evaluating habitat use and economic tradeoffs. Eligibility hinges on an Established Reef Ecosystem and compliance with plan criteria; a Reef Planning Area is designated within 90 days of eligibility, and final Reef in Place approval is due within three years after eligibility, pending meeting set conditions.

Section 5(e) (Outer Continental Shelf Lands Act amendment)

Artificial reefs—removal orders and liability provisions

Section 5 adds an Artificial Reefs subsection to the OCS Lands Act, tying the reefing framework to the broader regulatory regime. It defines terms used across the act for cross-reference, prohibits Removal Orders during defined windows tied to Notice, assessment, pending determinations, and appeals, and outlines liability transfers to States once an Eligible Structure is incorporated into a State Program. It preserves pipeline- and decommissioning-related processes under existing regulations and clarifies when a reefing activity becomes the legal responsibility of a State.

At scale

This bill is one of many.

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Who Benefits and Who Bears the Cost

Every bill creates winners and losers. Here's who stands to gain and who bears the cost.

Who Benefits

  • Offshore lessees and operators who elect Reef in Place for eligible inactive structures, potentially reducing long-term decommissioning costs and liabilities.
  • State Reef Programs that assume liability and receive cost-sharing opportunities, enabling coordinated oversight and maintenance.
  • Commercial and recreational fishers who gain enhanced habitat and potential fishing opportunities.
  • Coastal communities and tourism operators that benefit from improved ecosystem health and fishery yields.
  • Federal agencies (NOAA and Interior) that gain a structured, auditable framework for habitat restoration and decommissioning decisions.

Who Bears the Cost

  • Applicants (lessees/operators) responsible for assessments, compliance, and potential tail-end obligations unless cost-sharing is negotiated.
  • State programs that absorb liability and ongoing maintenance costs, albeit with funding offsets.
  • Federal agencies that shoulder administrative oversight, reporting, and interagency coordination.
  • Localities that may incur initial monitoring and marker-installation costs where applicable.
  • Potential costs to ensure navigational safety and markers in reefing zones, which may be borne by operators or states depending on the arrangement.

Key Issues

The Core Tension

The central dilemma is balancing ecological and economic gains from reefing inactive offshore structures against the costs, liability, and regulatory complexity required to implement Reefing in Place without compromising navigational safety or decommissioning timelines.

The act creates a multi-layer oversight structure that coordinates the Director, Administrator, and State Reef Programs. While it provides a clear pathway to convert inactive structures into artificial reefs, it also introduces procedural complexity, potential delays, and funding considerations.

The framework relies on assessments of habitat value, cost comparisons for reefing versus decommissioning, and the transfer of liability to State programs, all of which could affect project timelines and budgets. There are safeguards to preserve existing regulatory processes, but the regime raises questions about liability, long-term funding, and how State programs will be funded and managed when multiple structures are involved.

A key implementation challenge is ensuring robust, scientifically sound assessments within tight windows and harmonizing diverging state capabilities with federal requirements. The interaction with ongoing decommissioning obligations, navigational safety, and marker requirements also creates practical questions for operators and regulators alike.

Finally, the bill preserves other reefing avenues, which means reefing in Place must compete with or complement existing programs, potentially sharing resources and oversight responsibilities across agencies and states.

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