Economic Instruments

AuthorJamie Benidickson
ProfessionFaculty of Law University of Ottawa
Pages302-319
302
CHAPTER 17
ECONOMIC
INSTRUMENTS
1 OECD, Improving the Environment through Reducing Subsidies (1998).
A. SOME BASIC PROS AND CONS
Economic instruments, another of the more recently prominent
approaches to environmental protection, take a variety of forms. Not
all of the economic incentives currently in place or under considera-
tion are particularly innovative, even though efforts to appreciate the
environmental implications of their operation have intensified in the
past few years. Nor is the focus entirely on initiatives that are explic-
itly directed at improving environmental conditions, for the environ-
mentally-adverse impacts of other policy measures is of equal
significance. A simple example is subsidies to the agriculture, energy,
transportation and industrial sectors which have encouraged waste,
pollution and excessive natural resource consumption.1Although this
is an important matter, it will not receive much attention here.
After discussing the general attractions of economic instruments
and market mechanisms from an environmental perspective, as well as
noting some of the reservations that are expressed about them, this
chapter describes non-tax instruments, tax incentives, and public
funds dedicated to the environment. The chapter concludes with ref-
erence to insurance and financial institutions in light of their potential
Economic Instruments 303
2Environment Act, S.N. 1995, c. E-13.1, s. 21.
to use economic incentives in the interests of environmental protec-
tion.
Proponents of economic incentives anticipate that environmentally
appropriate behaviour can be encouraged if environmental costs are
properly priced and appropriately allocated. Certain elements of the
legal regime can be seen as consistent with an economic approach to
regulation. For example, statutory arrangements assigning financial
liability for clean-up costs and other expenses to “persons responsible”
for the damages express the general intention that the burden of com-
pensation for environmental losses should be borne by those who
stand to benefit from the activity that resulted in the damage. Profit-
stripping provisions are expected to eliminate the financial attraction
of disregarding environmental protection requirements. Legal imple-
mentation of the “polluter pays” principle is also often assumed to cre-
ate incentives for preventive measures and alternative approaches that
serve to avoid environmental harm in the first place. Such an observa-
tion might be made in connection with the following provision from
Newfoundland legislation:
Where pollution occurs and the person or municipal authority that
the minister considers responsible for the occurrence of the pollution
fails to do the things that the minister considers are appropriate to
prevent, control, eliminate or ameliorate the pollution, the minister
may take appropriate action to prevent, control, eliminate or amelio-
rate the pollution and the costs incurred by the minister in taking
that action are a debt due the Crown and are recoverable from the
person or municipal authority that the minister considers responsible
for the occurrence of the pollution.2
Although there are certain satisfactions in requiring those who pol-
lute to assume the costs of the damage they have caused, prevention is
more attractive. In general, advocates of economic instruments expect
not only that harm to the environment will be less likely when those
benefiting from the harmful activity must assume the costs, but that
society’s overall costs of achieving a given level of environmental pro-
tection will be lower because of a more efficient distribution among
polluters of the costs of meeting that standard. It is also anticipated
that appropriately designed economic incentives will promote the
development of innovative means to safeguard and improve environ-
mental quality on an ongoing basis.

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