Dear Editor,
The debate on oil-spill liability is being framed too narrowly. The issue is not whether Guyana is protected only by an unlimited parent company guarantee; the issue is whether the country now has a broader legal, regulatory and operational framework that allocates liability, compels prevention, strengthens response capacity, and preserves the state’s enforcement leverage. In a small, open, oil-producing economy, that distinction is not semantic. It determines how environmental risk is transmitted into fiscal risk, reputational risk, and wider balance-of-payments exposure. Taken together, the Petroleum Activities Act 2023, the Oil Pollution Prevention, Preparedness, Response and Responsibility Act 2025, and the strengthened EPA permit regime indicate that the architecture is materially stronger than the one that existed before.
The prevailing view misses the central point. An unlimited guarantee, by itself, is not the full liability regime. It is one financial assurance mechanism within a wider system of statutory obligations, permit conditions, operational controls, indemnities, insurance requirements, and ministerial enforcement powers. This author has argued previously that the legal and accounting treatment of environmental contingent liabilities must be assessed within that broader framework, not through a politically convenient but analytically incomplete narrative. The narrow interpretation fails to account for how modern petroleum governance actually works: prevention reduces probability, containment reduces scale, enforceable obligations reduce moral hazard, and a layered framework reduces residual exposure to the State.
In this regard, the Petroleum Activities Act 2023 materially strengthened the State’s position. Part XIII establishes the statutory framework for safety, risk management and emergency preparedness. Sections 73 to 76 are especially relevant. They provide for safety requirements and standards, require facilities and infrastructure to be maintained in a safe condition, empower the Minister to require remedial action or discontinuance of operations where there is an unacceptable risk of pollution or major damage, require risk assessments and safety management systems, and require emergency preparedness and response measures aligned with national or regional spill-response plans, with regular testing of those measures. Sections 87 and 93 are also critical, since they preserve ministerial monitoring and inspection powers and require the licensee to keep the state indemnified against claims and demands arising from the exercise of petroleum rights, while maintaining insurance as required by law.
The Act also goes beyond spill response in the narrow sense by creating an end-to-end environmental liability framework across the life cycle of petroleum operations. Part IX requires decommissioning plans and budgets, establishes a decommissioning fund, provides for post-decommissioning verification, and makes clear that failure to submit a decommissioning plan or meet decommissioning obligations does not relieve a licensee of liability for those costs. That is not a minor detail.
It shows that environmental liability in Guyana is no longer being treated as an afterthought at the point of incident; it is being embedded into the economics and governance of the project from production through abandonment. The broader framework shows that liability is being internalised ex ante, not merely debated ex post.
More importantly, Guyana has now enacted a bespoke oil-spill statute: the Oil Pollution Prevention, Preparedness, Response and Responsibility Act 2025. The significance of that enactment should not be understated. A dedicated oil-pollution law moves the country beyond reliance on fragmented permit language and general environmental principles alone. It provides a specialised legislative basis for prevention, preparedness, response, responsibility and cost recovery in relation to oil pollution events. In other words, the legal architecture has been widened and deepened. That is the opposite of a regulatory retreat.
The regulatory instruments have also improved materially, and the documentary comparison is decisive. The renewed EPA permits introduced substantive clauses that were absent from the earlier permits, including a project community grievance mechanism; mandatory recording and reporting of environmental grievances; tighter air-quality requirements tied to specified American Petroleum Institute standards; explicit restrictions on flaring, including approval thresholds and time limits; a carbon charge of US$50 per tonne of carbon dioxide equivalent for flaring above stipulated periods; stronger hazardous-waste controls; faster compliance deadlines for well safety case submissions; a requirement to maintain access to a capping-stack subscription service capable of mobilisation within nine days or less; express application of the polluter pays principle; NEBA and SIMA requirements for spill-response decisions; and entirely new sections on chemical handling, marine ecosystems management, production operations and safety, emergency shutdown systems, gas detection, fire detection, and firewater systems.
The sections on financial assurance and liability for pollution damage and on institutional authority were also expanded. The issue must be examined relative to enforceability. Better permit drafting reduces ambiguity, shortens regulatory response time, strengthens compliance leverage, and improves the state’s capacity to intervene before an incident compounds into a materially larger environmental and fiscal liability.
That is not a cosmetic permit revision; it is institutional risk reduction.
Then there is the operational dimension, which is often underweighted in public commentary. Liability is only one side of risk management; containment capacity is the other. The strengthened permit framework now requires access to a capping-stack mobilisation service within nine calendar days or less of an uncontrolled event, alongside broader spill-response obligations grounded in the polluter pays principle, remediation, monitoring, and agency approval for higher-risk response techniques such as in-situ burning and chemical dispersants. The causation chain is straightforward: stronger ex ante controls reduce the probability of a major event; faster intervention reduces the duration of uncontrolled discharge; shorter discharge duration reduces the scale of marine and coastal contamination; and lower contamination reduces remediation costs, compensation claims, and wider economic disruption. This must be assessed within the context of a small, open economy where a major spill is not merely an environmental issue but a fisheries, tourism, trade and fiscal-risk issue.
Accordingly, the claim that Guyana is inadequately protected unless the debate is resolved solely through an unlimited parent company guarantee is not a complete reading of the present framework.
The country now has a layered system comprising statute, materially strengthened permit conditions, emergency-response obligations, indemnity and insurance requirements, ministerial enforcement authority, and operational spill-containment measures. The determining factor is not whether one instrument can be rhetorically elevated above all others, but whether the total system is stronger, more enforceable, and more capable of reducing both the probability and the cost of environmental harm. On that test, the current framework is materially more robust. This is not merely a legal drafting issue; it is a question of sovereign risk management, environmental resilience, and national economic protection. In light of the foregoing, the proper test is not theoretical absolutes but whether Guyana’s current framework materially improves the state’s ability to prevent, contain, remediate, and recover. It does.