philosophy – Real LexEcon

Why System Thinking Requires Stricter Development Standards

Recent public discussions have reflected different perspectives on the Monterrazas development in Cebu City, including system-level explanations, precautionary considerations, and calls for regulatory review. These illustrate the complexity of decision-making in such contexts.

At first glance, the issue may appear as a familiar tension between development and environmental protection. However, it may be more accurately understood through a different lens.

From an economic perspective, what this situation reflects is a form of the Tragedy of the Commons.

The concern lies in understanding how multiple developments interact within a shared system, and how each contributes to cumulative impacts over time.

Cebu’s upland areas perform essential ecological functions. They absorb rainfall, regulate runoff, and contribute to the stability of downstream communities. These functions do not operate within the boundaries of individual properties. They extend across space, linking different parts of the city through continuous hydrological processes.

In this context, the question of whether a particular development lies within or outside a defined watershed boundary, while relevant in technical terms, does not fully resolve the issue. Environmental systems do not operate as isolated compartments. Their behavior reflects interaction rather than separation.

The scale of that interaction is often difficult to grasp in abstract terms.

Evidence from watersheds within Metro Cebu further clarifies how this system operates—and how development must be understood within it.

Studies of the Mananga watershed show that land-use and land-cover changes—particularly in upstream areas—affect infiltration, surface runoff, and the movement of water across the system. As vegetation is reduced or land is altered, less water is absorbed and more becomes surface flow.

A similar pattern is observed in the Butuanon River watershed. The river originates in upland areas of Cebu City and flows through increasingly urbanized zones before reaching the coast. Upstream areas are already characterized by agricultural and altered land uses, while downstream sections are densely developed. This configuration illustrates how water accumulates as it moves across elevations, shaped by both upstream conditions and downstream constraints.

Altogether, these cases point to a consistent principle:

The watershed is the system within which individual projects must be considered, as runoff is generated across the entire catchment while its behavior is shaped by land-use conditions across different elevations.

This framing is critical. It does not assign causation to any single location. Rather, it defines the proper unit of analysis.

A project is not evaluated in isolation, but in relation to the system it enters—where each intervention contributes to cumulative pressures and must therefore be assessed with reference to the system’s capacity.

It is often observed that flooding in Cebu is multi-causal. Infrastructure limitations, watershed conditions, land-use changes, and rainfall patterns all contribute. This observation is correct.

However, its implication must be properly understood.

If multi-causality is interpreted to mean that no single development can be meaningfully evaluated, then responsibility becomes diffused. Multiple factors contribute, yet accountability becomes less clearly defined.

But the correct implication is the opposite.

If risk is systemic, then evaluation must also be systemic—and correspondingly more rigorous.

The system is not an excuse—it is the basis for stricter evaluation.

This requires a shift in how development decisions are made.

The relevant question is not whether a particular project can be shown to cause a specific flooding event. Rather, it is whether the addition of that project contributes, in combination with others, to increasing pressure on a system that may already be approaching its limits.

The concern lies in the combined effects within a shared system, and in how each individual project contributes to those cumulative impacts.

This leads to a central question:

What is the capacity of the system?

How many developments are already present within a given environmental zone?
To what extent has land use already been altered?
At what point does additional development begin to significantly affect the system’s ability to absorb rainfall and regulate runoff?

Without a clear understanding of these limits, development decisions are made incrementally, without reference to cumulative thresholds.

The Monterrazas issue, therefore, should be viewed in terms of how development decisions are made when each additional project contributes to a system with finite capacity.

In such a context, compliance at the project level is no longer sufficient. Each additional intervention must be evaluated in relation to the condition of the system as a whole.

This has significant implications for urban development.

First, evaluation must move beyond individual projects toward system-level analysis.

Second, development must be aligned with capacity. Growth is no longer simply a matter of feasibility or compliance, but of whether the system can sustain additional pressure.

Third, planning must shift from reactive to anticipatory. Addressing impacts only after they occur is both inefficient and costly.

Fourth, institutional coordination must ensure that decisions reflect a consistent understanding of cumulative risk.

The Monterrazas issue is not resolved by determining whether it falls within a particular boundary, nor by isolating it from broader conditions.

It must be understood as part of a system where effects accumulate, capacity is finite, and each development contributes to increasing pressure on that system.

It shows that outcomes in shared systems are shaped not only by individual decisions, but by how those decisions accumulate—and whether they are governed by a clear understanding of limits.

Ultimately, the question is not whether a particular project should proceed or not.

It is whether each project is evaluated in light of the system it enters—and whether that system can sustain the additional burden it brings.

Because in such systems, urban development is no longer simply about what can be built.

It is about how each development contributes to a shared environment—and whether the whole remains within its capacity to endure.

On October 26, 2025, the tailing pond of the URC Bais Distillery collapsed. As a result, thousands of cubic meters of molasses wastewater spilled into the Tañon Strait. This spill polluted over 3,000 hectares of marine waters between Negros Oriental and Cebu. The spill killed fish and discolored the water. It forced tourism operators in Bais and Manjuyod to suspend dolphin-watching and sandbar activities. What unfolded was more than an ecological crisis. It was an economic crisis as well. This crisis rippled through coastal communities. Their livelihoods depend on clean water, healthy fish stocks, and tourism income. Yet, despite the extent of the damage, there has been no official economic valuation. Without valuation, harm remains visible to the eye but invisible to the law.

Economic valuation is not about assigning a price to nature. It is about recognizing the real value of ecosystem services that sustain livelihoods and well-being. It transforms abstract losses into measurable, actionable data that policymakers and courts can use to demand accountability and rehabilitation. In the absence of valuation, justice often fails to materialize. The Clean Water Act requires the government to quantify and integrate environmental costs into planning and policy. The Philippine Ecosystem and Natural Capital Accounting System (PENCAS) Act also imposes this duty. However, in many cases these studies are never conducted. As a result, environmental disasters become administrative events instead of economic wrongs.

This failure is not theoretical. In the case of Ang Aroroy ay Alagaan, Inc. v. Filminera Resources Corp., environmental advocates in Masbate filed a petition. They aimed to stop gold mining operations. These operations were alleged to have caused water pollution and marine degradation. The case was dismissed. The petitioners did not provide scientific evidence linking the mining activity to the harm. They also failed to provide valuation evidence. The courts held that while the right to a balanced and healthful ecology is self-executory, it cannot rest on speculation. Without measurable data, there was no causal proof, and therefore no justice. This shows that when environmental damage is not quantified, the legal system has nothing to compensate. It has no foundation to impose liability. There is also no guide to direct restoration.

The law, however, provides a way to act amid scientific uncertainty through the precautionary principle. This principle is enshrined in Rule 20, Section 1 of the Rules of Procedure for Environmental Cases. It allows courts to act even when causation is not fully proven. It shifts the burden of proof to the polluter once a prima facie case of environmental risk is shown. In the landmark case Resident Marine Mammals of the Tañon Strait v. Reyes, the Supreme Court ruled that complete scientific certainty is unnecessary. Action should not be postponed if it can prevent environmental harm. In practice, however, the Filminera case demonstrates that courts hesitate to apply this principle. This happens when there is no baseline data or valuation study to demonstrate measurable harm. The absence of valuation deprives the precautionary principle of its factual footing.

In the URC Bais Distillery spill, the Environmental Management Bureau itself confirmed the contamination of thousands of hectares. They also confirmed the presence of fish kills and the closure of tourism activities. These are not speculative claims—they are facts. The prima facie case for environmental harm already exists. Therefore, failing to conduct an economic valuation at this stage runs counter to the very spirit of the precautionary principle. The principle demands preventive and remedial action even amid uncertainty, and valuation is the mechanism that gives it economic expression. Quantifying losses in fisheries, tourism, and household costs is necessary not just to demand accountability. Estimating non-market ecosystem values is also essential to guide rehabilitation and compensation.

When valuation is absent, the government cannot compute what justice demands. Victims receive no restitution, ecosystems receive no quantified restoration, and polluters face no cost proportional to the damage they cause. Without numbers, there are no remedies. Without valuation, there is no justice. And without accountability, pollution becomes merely another cost of doing business. The precautionary principle tells us to act before harm becomes irreversible. For that action to have meaning, it must be backed by measurement.

The Tañon Strait is not just a channel between two islands. It is a living system that feeds communities. It attracts tourism and anchors the regional economy. Its value is not speculative but measurable. Government agencies such as DENR, NEDA, BFAR, and local governments have a duty. They must translate this value into policy through formal economic valuation. Only then can we ensure that environmental protection is not symbolic but substantial. The spill in Bais should be a turning point. It should teach us that when damage has no price, accountability disappears. To value nature is to defend it. To measure loss is to make justice possible.

To value nature is not to commercialize it but to defend it. Measurement gives law and policy their moral weight. When damage has no price, accountability disappears. But when we count every lost fish, canceled tour, and poisoned tide, we remind the nation that ecology is economy. Justice begins with knowing what we have truly lost.