When factoring a carbon price into an investment proposal, distinguish costs that will actually be paid from assumptions used for internal evaluation. An internal carbon price is a tool for comparing risks and emissions-reduction measures across business alternatives; it should not be treated as equivalent to the market price of tradable emissions allowances. The distinction is important when reading the discussion in Chapters 2 and 3 of Technology and Solutions for Demonstrating Carbon Reduction.
Define the concept and scope of application first
The purpose of a carbon price used for internal evaluation and the way it is applied should be stated. Cash flows differ depending on whether money is actually collected or the price is used only to evaluate investment alternatives. The two approaches should not be mixed in an evaluation table. If equipment has a long service life, its current price may not represent the entire period. Compare different assumptions about prices and cost pass-through, and show the point at which the ranking of alternatives changes. Sensitivity analysis is a tool for identifying how vulnerable a choice is, rather than for getting a forecast exactly right.
When responding to a range-based target, it is better to compare several implementation conditions than to rely on a single forecast. A reduction rate for the country as a whole should not be transferred directly into an individual farm’s required reduction rate. Assume that sectoral policies and trading conditions may change, and examine the effects on energy and feed prices and data-submission costs. Decide in advance what changes would prompt a review of equipment investment or business scale.
Investment priorities in livestock should be assessed together against cost per tonne, feasibility, and sufficiency of evidence. National inventories, corporate emissions inventories, and credits serve different purposes and have different recognition procedures. Direct measurement at every farm is not required; activity data, emission factors, and models allowed by the relevant system can be combined with quality management. Measurement infrastructure is an investment that improves confidence in those calculations. Keep physical emissions reductions distinct from recognition under a scheme, while preparing from the start of the project the data needed to connect the two.
Sensors and data systems provide a foundation for that assessment. The number of devices installed or the volume of data collected cannot stand in for emissions-reduction results. To avoid excessive measurement costs, first decide what decisions can change because of the new records and what level of quality those decisions require. Chapter 7 revisits evidence levels, and Chapter 19 revisits costs for farms and government.
An internal carbon price is a tool for incorporating assumptions about the costs associated with emissions into investment reviews. Varying the price level and facility lifetime can show the conditions under which the economics of a low-carbon alternative change.
A shadow price is used for evaluation without an actual transfer of funds, while an internal fee collects funds within the organization for uses such as emissions-reduction investment. Which approach is appropriate depends on the organization’s objectives and operating conditions.
A carbon price is both a number attached to emissions and a signal that redraws the industrial landscape. Yet for a long time this subject felt remote to Korean livestock farms and feed companies. Livestock farming is not covered by the emissions trading system, and there is no system that directly taxes livestock methane. This fact should be stated precisely: there is currently no carbon tax imposed directly on livestock farms in Korea.
Conditions and limits for field application
Suppose we are comparing two pieces of equipment with different energy use. The option with the lower purchase price may be more vulnerable to long-term changes in energy prices. An internal carbon price can be used to compare alternatives, but the evaluation should also show how their ranking changes when the price assumption changes. It would be inaccurate to say that a cost in an evaluation automatically becomes a cash outlay.
A carbon tax applies a tax rate to emissions subject to taxation and imposes a cost. If the rate and its adjustment path are specified, they can help establish price assumptions for an investment plan. The actual burden depends on the scope of application and any exemptions or relief. Setting a tax rate does not guarantee a particular volume of emissions reductions, so other policy instruments and actual responses should also be considered.
An emissions trading system sets a cap on the total emissions allowances available to covered entities and permits allowance trading. The price is formed through trading, and actual emissions do not necessarily match the cap exactly each year. Whether banking, borrowing, or the use of external reduction credits is allowed also depends on the rules of the relevant system.
Managing a cap on permitted emissions is the central advantage. However, actual reduction outcomes depend on how stringent the cap is, the scope of coverage, and the management of quantification and compliance. Economic conditions, fuel prices, and policy changes can shift allowance demand and prices, so a price decline may weaken incentives to invest in emissions reductions. The types of market-stability mechanisms and the conditions under which they operate should also be checked for each system.
Evidence needed for investment review
An investment review should check the source of the price, the period over which it applies, the emissions boundary, and the conditions for passing costs through. Assumptions can be set high to make a particular alternative look favorable, or reduction volumes can be overstated to make the cost per tonne look lower. Review the sensitivity of the assumptions alongside the conditions for actual implementation.
What farms and feed companies actually need to prepare is not to buy emissions allowances, but to identify which items in their own cost structures are exposed to carbon pricing. Tracking electricity use, chemical fertilizer use, transport distances and modes, and types of packaging can help estimate the direction and scale of cost changes over the next few years. Without this estimate, when prices rise you will not know the cause; without knowing the cause, you cannot respond.
The key point is that a product’s embedded emissions can be connected to the cost of trade. CBAM is a system that reflects carbon pricing in the embedded emissions of covered imports, making the quantification, reporting, and verification of related emissions data a supply-chain task. The responsible parties, covered goods, and implementation dates must be checked against the relevant rules. When discussing implications for agri-food, distinguish the current scope of application from the possibility of future expansion.
Criteria to keep in view when making a decision
A carbon price is not a formula that determines investment priorities with a single number. First check safety obligations, financial capacity, and the evidence for expected effects, then compare outcomes under different price assumptions. When alternatives are compared on the same basis, the price provides information needed for the decision.
About the author
Bongjun Lee graduated from the Graduate School of Management of Technology (MOT) at Sogang University. He spent seven years at Infitron Co., Ltd. and 20 years at Honeywell, working for a total of 27 years in gas measurement in service engineering, technical sales, and channel management. He is now the founder of AI Safety Korea Co., Ltd., where he is researching livestock methane monitoring and measurement, reporting, and verification (MRV) systems using sensors, AI, and data analytics.