When Science Becomes a Pretext for Administrative Evasion

Taiwan’s Biochar Carbon Removal (BCR) Governance Gap

Introduction｜When science stops being a tool for deliberation and becomes a language of bureaucratic avoidance

During the recent visit to Taiwan by the European Biochar Certificate (EBC) leadership delegation—at a seminar hosted by Guangtai—I felt, with unusual clarity, what the real risk facing Taiwan’s Biochar Carbon Removal (BCR) industry is.

It is not the absence of a market. It is a more difficult and ultimately more lethal non-technical structural problem: decision-makers’ fear of uncertainty is overriding scientific and institutional rationality.

At the event, it was reportedly suggested by a senior policymaker that “using biochar for agricultural sequestration may affect soil microbes, earthworms, and soil ecology,” and that this possibility justified a negative stance toward agricultural application. On the surface, this sounds like scientific caution. In practice, it often functions as a policy shortcut: inflate a possibility into a conclusion, then convert that conclusion into administrative paralysis.

Equally concerning, another official with an academic background reportedly questioned BCR by asking: “Verra’s international methodology has existed for quite some time—why haven’t we seen real projects?” This line of reasoning quietly implies that “no cases” means “no feasibility” or “no need to activate governance.” But it ignores an obvious institutional reality: methodologies do not become projects by themselves. Projects require enabling conditions—regulatory pathways, pilot permissions, supply-chain control, verification capacity, and credible MRV. Without pilots and institutional design, there will be no cases; without cases, the absence of cases is then used to argue that pilots should not be allowed. This is the self-reinforcing zero-case trap.

The core question is not whether any technology can guarantee “zero risk forever.” The real question is: when faced with a technology whose risks can be tiered, monitored, verified, and improved through pilots, does the competent authority build guardrails—or does it lock the door? In modern public governance, “prudence” does not mean pre-emptive rejection. It means decomposing uncertainty into manageable conditions and creating a pathway where society can learn, rules can iterate, and responsibilities can be borne transparently.

In materials-based climate solutions like biochar, international practice has already moved in this direction. Frameworks such as EBC, WBC, and IBI operationalize uncertainty through clear process controls, product testing, and use-based tiering—turning scientific uncertainty into administrative manageability, not an excuse for delay.

As someone working in this domain overseas, I have seen how multiple countries move from pilots to regulation, and from regulation to markets. This is why Taiwan’s real loss will never be “one fewer project.” It will be the loss of a narrow historical window to build governance capacity, influence standards, and secure a position in the emerging global division of labor for CDR. This paper advances a straightforward claim: the problem is not biochar—it is Taiwan’s underdeveloped ability to make responsible decisions under uncertainty. And that ability can only be built—slowly, painfully—through those willing to pilot, measure, and let data speak.

I. Clarifying the scientific baseline: Does biochar constitute “systemic ecological harm” to soil?

This debate cannot proceed without cleaning up the language. The policy claim often heard is: “Biochar in fields will affect microbes and earthworms, and may damage soil ecology.”

That single sentence conflates three very different ideas:

1. Any external input can alter a soil system.
2. Alteration is not the same as harm.
3. Harm must be established through reproducible, measurable evidence.

Biochar is not a single substance; it is a category of materials. Feedstock, pyrolysis temperature, residence time, and post-treatment can produce wildly different properties. This is precisely why serious governance systems—EBC being a leading example—are so widely referenced: they translate biochar into governable parameters and risk conditions through rigorous process requirements and use-based categories.

I.1 What the literature generally supports—and what it does not

To date, mainstream international research does not support the sweeping claim that “properly produced biochar, applied at reasonable rates, causes broad or systemic harm to soil ecosystems.” Much of the evidence instead shows that biochar tends to change soil environments in ways that can be neutral, positive, or context-dependent—depending on material properties, soil type, application rate, cropping system, and baseline pollution load.

Common findings frequently include:

• Soil physical/chemical improvements: porosity, water retention, aeration, and cation exchange capacity may improve, particularly in degraded soils.
• Habitat effects for microbes: porous structures can provide micro-habitats; shifts in microbial communities are often observed—but “change” is not “collapse,” and certainly not “systemic harm.”
• Adsorption and toxicity reduction: biochar can bind certain organics, pesticide residues, and heavy metals, lowering bioavailability and reducing exposure pathways that actually drive ecological injury.

The scientifically defensible conclusion is not “no risk exists.” It is: effects and risks are conditional, classifiable, monitorable, and manageable—not inherently veto-worthy. That is exactly what frameworks like EBC are designed to operationalize: not a fantasy of zero risk, but a governance language that allows policy to act responsibly.

I.2 The most damaging logical break in Taiwan’s debate: “possible impact” becomes “do not touch”

If “possible impact on underground biota” is treated as a veto threshold, then Taiwan must apply the same standard consistently. Two long-standing agricultural realities would, under that logic, require much more urgent action:

• Chronic chemical pesticide and fertilizer use with well-established exposure pathways and ecological impacts;
• Post-harvest burning and the ash/char residues that enter soils from uncontrolled combustion—materials that are far less standardized, traceable, or verifiable than regulated biochar.

Yet these are often treated as normal practice, while regulated, measurable, and controllable biochar is framed as uniquely threatening. From a risk-governance perspective, this is inverted logic:

The less controllable the behavior, the more normalized it becomes;

the more controllable the new technology, the more it is treated as a threat.

The real question, then, is not “will biochar hurt earthworms?” but whether Taiwan is willing to adopt use-based tiering and verification practices—like EBC’s approach—to move the debate from rhetorical possibility to operational standards and measurable outcomes.

II. The real institutional problem: how “uncertainty” becomes a veto mechanism

If Section I clarifies that biochar is not “guilty by nature” and can be governed through tiered conditions, then Section II must address the uncomfortable core: Taiwan’s bottleneck is frequently not a lack of science, but a lack of willingness to convert science into executable governance.

In public policy, uncertainty is not an exception—it is the default. Mature governance responds with a predictable sequence:

pilot at small scale → monitor and verify → codify evidence into rules → scale responsibly.

That is how systems like EBC and IBI function: they do not wait for perfect certainty; they translate uncertainty into conditions that can be managed.

Taiwan, however, too often follows the reverse pattern:

uncertainty becomes a reason not to govern—rather than the very object governance is meant to manage.

II.1 The “zero-case trap”: no pilots, no data, no cases—therefore no pilots

A familiar loop emerges:

• “There might be risk, so let’s not do it yet.”
• No pilots → no data → no cases.
• “There are no cases, therefore it’s not mature / not worth enabling.”
• Back to step one.

This is rational inside a bureaucracy because incentives are distorted:

• Allowing a pilot creates visible accountability risk.
• Refusing a pilot typically carries near-zero cost—often reduced to “we will continue studying.”

That is not scientific conservatism. It is a responsibility allocation failure: doing something creates personal downside; doing nothing rarely does.

II.2 Why BCR is especially easy to stall

BCR triggers three structural pain points:

1. Cross-ministerial overlap: agriculture/forestry, environment, industry/energy, and construction. When responsibility is diffuse, everyone can comment, but no one wants to sign.
2. Materials-based complexity: “Is it safe?” cannot be answered without specifying feedstock, process, dose, soil type, use case, monitoring requirements. Mature systems govern by decomposing; immature systems default to “too complex—wait.”
3. No incumbent protection: entrenched practices persist despite risks; new solutions lack political shelter and become the cheapest target for veto-by-caution.

II.3 Where scientific caution belongs: as guardrails, not as brakes

A blunt line must be drawn:

If scientific uncertainty can only be used to block pilots, it stops functioning as science and becomes politics.

The correct institutional use of scientific concern is to translate it into:

• Tiered governance by use case and quality class;
• Pilot provisions with limits on scale, site, time, and monitoring;
• Traceability and verification through process data, testing, third-party audits, and long-term monitoring.

That is the governance muscle Taiwan needs—not perpetual postponement.

III. Feedstock constraints and use-based tiering: Taiwan’s “precision + ICT + integrity” BCR strategy

Taiwan’s sustainable biomass supply is indeed limited. Viable sources under regulatory and sustainability constraints tend to be agricultural residues, pruning/woody waste, and manageable bamboo resources. This reality should not be sugarcoated—nor should it be weaponized as “therefore we should not do BCR.”

In policy terms, limited feedstock is not a veto rationale; it is a design constraint. It does not mean “impossible.” It means “choose the right positioning.”

III.1 Taiwan should not pursue a low-price, high-volume, agriculture-first route

Critics often treat limited feedstock as a final verdict: Taiwan cannot build BCR. That assumes only one industrial model exists—mass volume, low unit price, and large-scale agricultural spreading.

But Taiwan’s industrial advantage has never been “bulk and cheap.” Taiwan’s strength is:

precision process control, advanced equipment, materials engineering, ICT-enabled monitoring, and auditable supply chains.

Limited feedstock therefore implies a different strategy:

• Not a “tons-at-all-costs” agricultural route;
• But a small-scale, high-integrity, higher-value route—where price is earned through verifiability and governance.

In the CDR economy, the truly expensive commodity is not carbonized material. It is integrity.

III.2 Scarcity should force smarter allocation—through use-based tiering

If feedstock is scarce, it should not be allocated to the lowest-value or most politically vulnerable path. It should go where:

• environmental benefits are measurable,
• risks are controllable,
• markets can sustain pricing, and
• MRV and verification costs are feasible.

This is exactly why use-based tiering matters: it turns a material into a governable asset class.

III.3 “No cases exist” is not evidence of infeasibility—it is evidence that pilots are blocked

The “methodology has existed but no projects exist” argument is a classic zero-case trap. BCR requires controlled sourcing, controlled production, quality testing, clear use-boundaries, monitoring, third-party verification—and, critically, a regulatory pathway that allows pilots to connect these elements in the real world.

No pilots → no cases.

No cases → used to deny pilots. That is governance failure, not technology failure.

III.4 Taiwan’s winning play: convert “limited feedstock” into “precision + ICT + exportable integrity”

If Taiwan aims to be internationally credible in BCR, it should compete on integrity, not volume. But “integrity” here is not ESG messaging. It is Taiwan’s hard power:

precision manufacturing, equipment engineering, ICT data governance, and system integration.

A high-probability strategy looks like this:

• Use mature frameworks (EBC/IBI-class thinking) to define quality and use tiers;
• Build pilots as monitorable, verifiable, replicable templates—traceability, process data, testing, MRV, long-term monitoring, audit trails;
• Start with high-control applications (industrial, environmental engineering, construction materials) to build credibility, then expand to more sensitive agricultural pathways.

The core barrier is not engineering capacity. It is the absence of a governance window that allows engineering to land.

IV. Guangtai as a regulatory pioneer: why governance must protect—not exhaust—early doers

By now, the pattern is clear: biochar is not “naturally guilty,” risks can be tiered, feedstock scarcity favors high-integrity strategies, and the greatest policy error is forcing everything into the most sensitive agricultural debate. At this stage, the discussion must shift from “who is right in theory” to “does governance take responsibility.”

This is where Guangtai’s role must be reframed.

Guangtai should not be treated as a firm asking for special treatment. It is better understood as a rare and valuable figure in emerging climate industries: a regulatory pioneer—an actor willing to build real systems, accept pilots, accept verification, and let rules improve through evidence.

Such pioneers bear three costs simultaneously: engineering cost, regulatory cost, and reputational cost. Guangtai demonstrates three traits that governance should recognize and protect:

1. investing in real equipment and controlled processes, not paper-only narratives;
2. accepting the uncertainty and scrutiny of pilot-stage validation;
3. committing to standards, third-party verification, and long-term monitoring—seeking “controlled but feasible,” not “uncontrolled but fast.”

In emerging CDR fields, rules do not mature in isolation. Rules mature through real cases. If governance exhausts pioneers through indefinite procedural delay, it sends a devastating market signal:

Taiwan does not reward responsibility; it punishes the first mover.

The consequences are predictable: capital retreats, talent exits, and the market becomes dominated by those who tell stories rather than those who build verifiable systems.

V. Three immediately implementable governance designs (responsibility can be shared)

Taiwan’s blockage is not a shortage of standards, but a shortage of political will to deploy standards as governance. Here are three actions that can be implemented now—without waiting for “no controversy.”

V.1 Use-based tiered regulation, not blanket technology rejection

Separate governance by use category, with different entry conditions and oversight intensity:

• Industrial applications (adsorption, pollution control, material modification): highly controllable, standardizable → priority pathway
• Construction materials (concrete, bricks, composites): clear boundaries, more feasible MRV → second wave
• Agricultural application: most sensitive, requires higher trust and long-term monitoring → conditional and phased approach

This replaces “one-size-fits-all fear” with precision governance.

V.2 Pilot provisions designed around measurable MRV

Formalize pilots as legitimate, supervised, and reversible policy instruments:

• limit scale,
• limit sites (prioritize high-control contexts),
• limit time (e.g., 12–24 months per phase),
• define MRV indicators up front and require records + third-party checks.

This moves policy from “fear-based decisions” to “data-based decisions.”

V.3 Responsibility sharing and explicit exit clauses

Many policies stall because signing creates unlimited downside while refusing creates none. Fix that incentive structure:

• joint approval across agencies,
• an independent technical committee with transparent records,
• explicit exit clauses: if indicators fail or measurable harm occurs, suspend or terminate according to pre-defined rules.

This makes governance bear risk institutionally rather than personally.

Conclusion｜Taiwan’s industrial ecosystem should not be destroyed by the absence of governance capacity

From an overseas perspective, Taiwan’s most painful loss is not limited resources or constrained feedstock. It is the unwillingness to use governance tools—tiering, pilots, monitoring, verification, iteration—to make responsible decisions under uncertainty.

Even more perverse, narrative-driven “nature-based” story-selling can sometimes proceed with far less scrutiny, while projects that actually invest in equipment, monitoring, and verification are suffocated by procedural delay. The market signal becomes inverted: storytellers thrive; builders are punished.

Biochar does not need to be mythologized, nor demonized. It needs what any normal state should provide when confronting a new technology:

a controlled space to try, evidence-based mechanisms to improve, and institutions that share responsibility rather than outsource it to delay.

If Taiwan cannot do even this, what is lost will not merely be one BCR pathway or one company’s opportunity. Taiwan risks losing its entry ticket to the next generation of global CDR governance, standard-setting, and industrial specialization.

And that cost will exceed any risk of “one more pilot.” Because the real question is not whether one experiment succeeds. It is whether a country still has the ability—and courage—to make responsible decisions under uncertainty, and to put science back where it belongs: as a tool of governance, not a pretext for avoiding it.