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Budget 2005 - Budget Plan Annex 4
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Environmental Costs,
Market Prices and Taxes
When markets are functioning properly, prices are a reliable guide to the cost of producing goods and services. This allows society to make the best use of its resources. But when producing or consuming a good imposes environmental costs not faced by producers or consumers individually, these additional costs are not factored into market prices. As a result, market prices for certain goods are too low, and more of these goods are produced or consumed than would be the case if decision makers took into account the environmental costs that have to be borne by society at large. For illustrative purposes, the case of an industrial process that causes pollution (e.g. release of toxic substances) is depicted, in simplified form, in the adjacent chart. If firms decide how much to supply (based on demand and the cost of labour, materials and capital) and do not consider environmental costs that they do not have to bear, the free market equilibrium (A) is not optimal. Assuming each unit of production creates the same amount of pollution, the supply curve that would apply if the producer had to bear the environmental costs is an upward rotation of the market supply curve, indicating a lower level of production at all prices. One approach to improving the market outcome is to impose a tax on production. If the Government sets the tax at the right level, the new equilibrium will occur at a point (B), where prices reflect the private costs of production as well as the environmental costs. The quantity produced and consumed is then reduced from Q0 to Q1. Resources (labour and capital) not used may then be deployed more efficiently to other uses. Whether such an illustrative example may be applied in practice depends, case-by-case, on a broader range of factors such as those set out in the framework described in this annex. |
Economic instruments encompass a range of tools that have been used in specific circumstances, both in Canada and internationally, to advance environmental goals. Some of these tools are broad-based, affecting transactions across a range of products, technologies, or sectors of the economy. Others are more targeted. In addition to the tax system, the tools include tradable permits, grants and subsidies, and government procurement policy (see box below).
Economic Instruments
for the Pursuit
of Environmental Goals—Examples
Tax measures can be structured as either incentives or disincentives to induce a change of behaviour on the part of producers or consumers in favour of more environment-friendly goods, services, or activities. Federal environmental tax measures implemented in recent years include accelerated capital cost allowance for energy efficient and renewable energy generation equipment (Class 43.1), which is enhanced in Budget 2005, excise tax relief for alternative fuels, and a reduced inclusion rate on capital gains for donations of ecologically sensitive land. A system of tradable permits may be used to limit the amount of pollution emitted by firms. After an initial allocation, these permits can be purchased and sold by firms. Firms with relatively low pollution abatement costs have an incentive to reduce their emissions and sell excess permits to firms that have higher abatement costs. As a result, only the most efficient methods of abatement are used, minimizing the cost of achieving the mandated reduction. In January 2005, the European Union Greenhouse Gas Emission Trading Scheme (EU ETS) commenced operation as the largest multi-country, multi-sector greenhouse gas emission trading scheme, worldwide. Grants and subsidies are payments designed to encourage the recipients to undertake specific environment-friendly activities. For example, Natural Resources Canada, through its EnerGuide for Houses Retrofit Incentive program, provides grants to Canadian homeowners who make retrofit improvements that increase the energy efficiency of their homes. The grants lower the cost of the retrofit and stimulate market demand for home insulation production and services. This program is expanded in Budget 2005. Procurement policies, such as the Government’s "Green Procurement" initiative, involve the practice of acquiring goods and services that minimize the use of natural resources, the use and production of toxic materials, and/or emissions of greenhouse gas and other air pollutants. The Federal House in Order (FHIO) initiative is the federal government’s plan for reducing greenhouse gas emissions (GHGs) within its own operations. Through this initiative, the 11 departments and agencies that account for 95 per cent of the Government’s GHG emissions have agreed to meet collectively a target of reducing greenhouse gases within their operations by 31 per cent, from 1990 levels, by 2010. |
Against this background, the use of the tax system covers two key types of interventions:
What is the
Polluter-Pays Principle?
The "Polluter-Pays Principle" is a concept that addresses the allocation of the costs of pollution prevention, control and remediation measures in a manner that encourages a rational use of scarce environmental resources. As a policy principle, it means that the polluter should bear the costs of activities that directly or indirectly damage the environment. This cost, in turn, is then factored into market prices. |
There are limits to the judicious use of the tax system to advance economic growth and a sustainable environment. It is not sufficient that a market failure be identified. In some cases, there may not be a specific measure that could be implemented effectively to correct for the market failure. Further, government intervention has its costs. It may give rise to unintended and/or undesirable consequences. It may generate other economic distortions, or be unfair to certain producers or consumers.
It is important that all such considerations be factored into the analysis of environmental tax proposals. Where a clear goal is established, proposed tax measures must be assessed against a set of criteria that must also guide the evaluation of alternative forms of intervention—including regulation, spending, and other economic instruments.
The basic role of the tax system is to raise revenue to fund government expenditures and to do so in a manner that is economically efficient, fair, and as simple as possible for compliance by taxpayers and administration by the government. The management of the tax system entails not only establishing the overall level of taxation in the economy, but also the structure of the tax system. This includes, for example, addressing how tax bases are defined, and how the tax burden will be shared among taxpayers.
Proposals for new environmental taxes may be assessed on a case-by-case basis, taking into account the following criteria.
Environmental effectiveness: whether, and to what extent, the proposal will contribute to achieving the environmental goal.
Fiscal impact: how the proposal will affect government expenditures or revenues.
Economic efficiency: how the proposal will affect the allocation of resources in the economy and Canada’s global competitiveness.
Fairness: how the impacts of the proposal are distributed across sectors of the economy, regions or groups within the population.
Simplicity: how governments will administer the proposal and how affected individuals or parties will comply—and at what cost.
Of course, there may be trade-offs among these different criteria that will require a decision, by government, on the relative weight to be applied to each criterion in making choices and establishing priorities.
As a general proposition, an environmental tax measure will be effective if it induces a change in producer or consumer behaviour that achieves the environmental goal. This presupposes that two key conditions can be met.
Effective targeting means that the measure can be designed to affect the transactions in the marketplace—and then, to the extent possible, only those transactions—that are germane to the pursuit of the environmental goal. For a tax measure, this requires that clear and objective parameters can be established in law to ensure that the tax incentive or disincentive will apply where it is most likely to make a difference.
In this regard, the tax system has some limitations. First, key parts of the tax system impact various segments of the marketplace differently. Specifically, income tax measures such as deductions or credits will generally affect only individuals or corporations that are, or may become, taxable. They will not affect entities like governments, Crown corporations, or non-profit organizations that do not pay income taxes. Similarly, corporations that do not have taxable income will tend to discount deductions or credits that have no immediate impact on their tax liability. Correspondingly, income tax measures may have a different value for different firms. This is in contrast to grants or subsidies that may be paid equally to all recipients. For example, whereas the Wind Production Power Incentive may be paid in the same amount to all producers, the value of accelerated capital cost allowance for the related capital investment will depend on whether the producer is in a taxable position today, or likely to be in the future. In contrast to income tax measures, excise tax measures (e.g. fuel excise tax relief for renewable fuels) may apply more evenly across market segments.
Second, the tax system is a relatively blunt instrument. The conditions of application of a tax measure are set in law, taxpayers are required to comply, and the Canada Revenue Agency administers the measure on that basis. As a general proposition, tax measures are not easily targeted to a very narrow segment of the market, or made to adapt to diverse circumstances or conditions. An expenditure program may be designed and administered in a manner that allows more discretionary application and narrow targeting to achieve a specific goal.
The effectiveness of an environmental tax measure depends on the sensitivity of demand and supply to changes in prices (see box for an illustration of this concept).
If a tax incentive is applied to a product for which demand is relatively insensitive to price changes, it will create "windfall" effects: the environmental benefit will be small and most of the fiscal cost will represent a transfer from taxpayers to purchasers of the subsidized product. In other words, a proposed tax measure that does not alter measurably the behaviour of producers or consumers will not be effective. An effective measure is one that will not simply reward good behaviour—although that may be considered appropriate in its own right—but one that will also induce a positive change in consumer or producer behaviour.
Financial Incentives,
Price Responsiveness and Environmental Effectiveness
The ability of a financial incentive, as may be provided by a tax measure, to affect consumer or business spending depends on the sensitivity of both demand and supply to changes in prices. For example, if consumer spending on home insulation is relatively sensitive to prices and there are no substantial supply constraints, a financial incentive can generate an increase in consumer spending on home insulation that will justify the fiscal cost. This situation is shown in Chart 1. Initially the market is at the point A, with a price Pm and a quantity Q0. A financial incentive is introduced that increases demand from Q0 to Q1 at the market price, Pm, since the net price to consumers, Ps, is reduced. This is illustrated by the rightward shift of the demand curve, which moves the market equilibrium point from A to B. The rise in spending depends only on the sensitivity of demand to price since additional supply is assumed to be available at prevailing prices. The fiscal cost of the incentive is determined by the total quantity consumed (Q1) multiplied by the subsidy rate (Pm- Ps). That is, all purchasers of home insulation benefit from the incentive, including those who would have made a purchase without it. If demand is less sensitive to price, or if the market price rises along with demand due to supply constraints, incentives become less effective. In particular, if market supply is highly constrained, producers will absorb most of the benefits of the incentive through higher prices, with only a small change in the quantity consumed. This situation is illustrated in Chart 2, which shows the market price rising from Pm0 to Pm1 along with a small change in demand from Q0 to Q1. The prospective effectiveness of the subsidy, as determined by the sensitivity of both demand and supply to price, is an important consideration in evaluating a proposed incentive. Comparing the cost of the subsidy to the induced change in spending gives a preliminary indication of cost-effectiveness. Everything else being equal, the greater the "leverage" of an incentive (i.e. the increase in spending relative to the fiscal cost) the greater will be its cost-effectiveness. In Chart 1, the increase in spending exceeds the cost of the incentive, while the opposite situation is depicted in Chart 2. |
Environmental tax measures will generally have an impact on tax revenues and the Government’s overall fiscal framework. For this reason, they must be assessed in the broader context of a commitment to balanced budgets, sound fiscal management and an efficient tax system.
A tax incentive represents foregone government revenue. In other words, it imposes a cost that, in a balanced budget context, must be offset by higher taxes, or reduced spending, elsewhere. The cost of a tax incentive may be difficult to estimate precisely because it depends on the degree of taxpayer take-up. This is in contrast to an expenditure program to which a defined amount of money may be allocated.
In comparing and ranking alternative proposals, it may be useful to evaluate the projected fiscal cost against the expected environmental benefits. For example, measures may be ranked by how many tonnes of greenhouse gas emissions reductions they produce per dollar of foregone tax revenue. Such comparisons may be carried out across tax and non-tax measures to help identify the most cost-effective environmental policy measures.
A tax disincentive may, alternatively, raise additional government revenue. This revenue will generally be deposited in the Government’s Consolidated Revenue Fund and be used to reduce other taxes, or to fund public spending.
Tax measures can be revenue neutral if they are structured in such a manner as to raise the level of tax paid by some taxpayers, while at the same time lowering the level of tax paid by others. Such an approach could be developed in respect of a set of measures that collectively would contribute to advancing environmental objectives while being neutral from a fiscal standpoint. While the result in terms of the total level of taxation could be neutral, it could be positive in terms of both environmental and economic efficiency outcomes (see "Economic Efficiency" below).
In some instances, there may be a case for directing some of the revenues of an environmental tax to a specific use—a concept generally referred to as "revenue earmarking." The rationale often cited by proponents of this approach is that the willingness of taxpayers to pay will be higher if there is a direct and transparent link between the incidence of the tax and the subsequent use of its proceeds (e.g. a tire tax to fund tire disposal costs).
From the Government’s perspective, however, in some circumstances earmarking may reduce fiscal flexibility and result in some programs being over-funded, and other priorities being under-funded.
Some proposed environmental tax measures—i.e. measures that affect the income tax base or the goods and services tax (GST) base—could have financial implications for provinces that share the same tax bases under agreements with the federal government.
In all cases, because of their fiscal dimension, proposals for federal environmental tax measures will generally be assessed in the broader context of developing fiscal priorities for the annual budget.
Aside from the fiscal cost or revenue, economic costs or benefits of a tax measure must also be assessed and related to environmental benefits. There are three key considerations: internal efficiency, competitiveness, and adjustment costs.
A key thrust of a policy to integrate environmental and economic factors into decision making is to identify environmental solutions that also contribute to improved economic performance. Where market failures can be identified, a well-targeted tax measure may provide improved price signals, contribute to a more productive use of resources, stimulate technological innovation, and hence improve the efficiency of the economy. Careful analysis is required to assess the market failure and to determine whether a tax measure can properly deliver the intended adjustment to prices. This will inform how the tax measure may affect the allocation of resources in the economy and productivity. The benefits of correcting an environmental market failure, however, may not always be captured in economic performance, as conventionally measured. In these instances, the loss in measured economic output must be compared to the benefits of a better environment, evaluated more subjectively.
An important, related consideration is how environmental tax measures may affect the structure of the tax system. Within a revenue-neutral framework, tax incentives would be offset by higher taxes elsewhere. Conversely, environmental taxes that generate revenue would allow reductions in other taxes. Analysis shows that different taxes impose different costs on the economy.[1] For example, taxes on consumption tend to impose lower economic costs than taxes on investment or saving. Correspondingly, environmental tax measures may generate added benefits or costs depending on whether their effect is to improve, or to lessen, the overall efficiency of the tax system.
Consideration must also be given to the impact—positive or negative—of a proposed measure on international competitiveness. This will include assessing the effect on both the overall level of taxation and the incidence of taxes on those sectors of the economy engaged in competition, at home or abroad.
By changing the behaviour of economic agents, tax measures will cause adjustments in the marketplace that may entail some costs. For example, tax measures that would reduce demand for a particular good will affect the producers of that good. The producers may respond by investing in new technology, or alternatively, by lowering production or shutting down their facilities. It is important that such scenarios be reviewed and that corresponding economic or social costs be identified.
The fairness of a proposed tax measure relates to the distribution of the burden of the tax, or of the benefit of the tax incentive.
Generally speaking, it is considered fair that polluters pay a tax, and that firms and consumers willing to adopt environment-friendly behaviour benefit from a tax incentive. Nonetheless, the application of tax measures may, in some circumstances, be perceived to affect or benefit disproportionately particular individuals, regions, or sectors of the economy. The assessment of distributional impacts is an important part of the evaluation that poses particular difficulties as it may bring trade-offs into play.
Tax measures will work best if they are relatively simple and can be easily understood by affected taxpayers.
Compared with spending programs or regulation, tax measures will tend to work best where the intention is to leave more of the decision making and responsiveness in the hands of producers and consumers. Through the use of a tax measure, the Government affects a price or another economic parameter, and it lets economic agents respond accordingly. In the best of cases, this minimizes bureaucratic involvement and promotes flexible, cost-effective responses by taxpayers.
However, if the targeting of the measure or its adjustment over time requires a complex set of rules, this benefit may be lost and the tax system—its design, administration and compliance—may become unwieldy. Costs for the Government to administer and monitor, and taxpayers to comply with a measure, may become prohibitive.
The pursuit of a productive, growing and sustainable economy requires that both environmental and economic considerations be integrated into decision making.
In this context, the case for government intervention in pursuit of environmental goals is founded in large measure on the need and opportunity to correct market failures. Where market failures exist, well-designed government intervention can foster a more rational use of resources and enhance both environmental and economic outcomes.
The Government has a range of policy instruments at its disposal. Important among these are economic instruments—including tax measures—that aim to leverage the capacity of the marketplace to respond to price signals, to innovate, and to contribute to the achievement of policy goals at the lowest cost.
Environmental tax proposals may be evaluated against five criteria: environmental effectiveness, fiscal impact, economic efficiency, fairness, and simplicity. With the benefit of a detailed evaluation, a tax measure may be shown, in some circumstances, to be the most appropriate policy instrument for addressing an environmental problem. In others, it may not be the instrument of choice.
For any environmental goal, it is important that consideration be given to all of the available policy instruments and that solutions be identified that produce the best results for the environment, at the lowest cost for taxpayers and the economy, and in the fairest and simplest manner. Sound fiscal management and the pursuit of an efficient tax structure will require that consideration be given to both tax incentives and tax disincentives.
Opportunities to use the tax system to advance environmental goals will continue to be actively considered. For this purpose, it will be necessary to engage stakeholders, non-governmental organizations and interested Canadians on the best means to promote sustainable growth. The framework set out in this annex is intended to facilitate this dialogue and to foster a shared understanding of policy considerations that may be taken into account as proposals are developed, assessed and implemented.
1 "Taxation and Economic Efficiency: Results From a General Equilibrium Model," Tax Expenditures and Evaluations, Department of Finance, 2004.[Return]
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Last Updated: 2005-02-23 |