Economic Instruments

AuthorJamie Benidickson
ProfessionFaculty of Law University of Ottawa
Pages358-378
358
CHA PTER 17
ECONOMIC
INSTRUM ENTS
Economic instruments, another of the more recently prominent ap-
proaches to environmental protection, take a variety of forms. Not all of
the economic incentives currently in place or under consideration are
particularly innovative, even t hough efforts to appreciate the environ-
mental implications of their operation have intensif‌ied in recent years.
Nor is the focus entirely on initiatives that are explicitly directed at
improving environmental conditions, for the environment ally-adverse
impacts of other policy measures i s of equal sig nif‌icance. A simple ex-
ample is subsidies to the agriculture, energy, transportation and in-
dustrial sectors which have encouraged waste, pollution and excessive
natural resource consumption.1 Although this is an important matter,
it will not receive much attention here.
After discussing the general attractions of economic instruments
and market mechanism s from an environmental perspective, as well
as noting some of the reservations that are ex pressed about them, this
chapter describes non-tax instruments, tax incentives, and public funds
dedicated to the environment. The chapter concludes with reference to
insurance and f‌inancial institutions in light of their potenti al to use
economic incentives in the interests of env ironmental protection.
1 OECD, Improving the Environment through Reducing Subsi dies (Paris: OECD,
1998); OECD, Environmentally Harmful Subsidies: Ch allenges for Reform (Paris:
OECD, 2005); OECD, Subsidy Reform and Sustaina ble Development: Economic,
Environmental and Soc ial Aspects (Paris: OECD, 2006).
Economic Instr uments 359
A. SOME BASIC PROS AND CONS
Proponents of economic incentives anticipate that environmentally ap-
propriate b ehaviour can be encouraged if t he env ironmental costs of
various activities are recognized, and then appropriately valued and
allocated. Certain elements of the legal regime c an already be seen
as consistent w ith an economic approach to regulation. For example,
statutory arrangements assigning f‌ina ncial liability for clean-up costs
and other expenses to “persons responsible” for the da mages ex press
the general intention that the burden of compensation for environ-
mental losse s should be borne by those who stand to benef‌it from the
activity that resulted in the damage. As t he Supreme Court of Canada
remarked in Imperial Oil, the polluter-pays principle “assigns pollut-
ers the re sponsibility for remedying contam ination for which they are
responsible and imposes on them the direct and immediate costs of
pollution.”2 In this regard, prof‌it-stripping provisions are expected to
eliminate the f‌inanci al attraction of disregarding environmental pro-
tection requirement s. Legal implementation of the polluter-pays prin-
ciple is also often assumed to create incentives for preventive measures
and alternative approaches that serve to avoid environmental harm in
the f‌irst place. Such an observation might be made in connect ion with
the following provision from Newfoundland legi slation:
Where pollution occurs and t he person or mun icipal authority that
the minister considers respon sible for the occurrence of the pollution
fails to do the things that the minister considers are appropriate to
prevent, control, eliminate or amel iorate t he pollution, the minister
may take appropriate action to prevent, control, eliminate or amelior-
ate the pollution and the costs incurred by the minister in taking that
action are a debt due the Crown and ar e recoverable from the person
or municipal authority that the minister considers responsible for the
occurrence of the pollut ion.3
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 i nstruments expect
not only t hat har m to the environment wil l be less likely when those
benef‌iting from the harmful activity must assume the costs, but that
society’s overall costs of achiev ing a g iven level of environmental pro-
tection will be lower because of a more eff‌icient distribution among
2 Imperial Oil v. Quebec, [2003] 2 S.C.R. 624 at 642.
3 Environment Act, S.N. 1995, c. E-13.1, s. 21.

To continue reading

Request your trial

VLEX uses login cookies to provide you with a better browsing experience. If you click on 'Accept' or continue browsing this site we consider that you accept our cookie policy. ACCEPT