Environmental Valuation and Compensation

AuthorJamie Benidickson
Pages215-230
215
CHAPTER 10
ENVIRONMENTAL
VALUATION AND
COMPENSATION
A. THE NATURE OF ENVIRONMENTAL
DA M AGE
Environmental damage and other losses suffered as a result of ongoing
pollution, accidents or spills, general degradation, or the over-exploita-
tion and mismanagement of resources may take many forms. Physical
contamination of a short- or long-term nature is an obvious example,
with or without destruction of plant and animal life, or biodiversity
loss. In severe situations it is also possible to imagine that contamina-
tion will have per manently or irreversibly undermined the regenerative
capacity or resilience of the affected ecosystem. Losses here may also
entail the reduction or elimination of what we are coming to appreci-
ate as ecological services such as water supply, climate stabilization,
nutrient cycling, or pollination. Insofar as human populations are con-
cerned, individuals may suffer adverse health effects, physical damage
to property, or economic losses, singly or in combination. On occasion
it is possible to speak of entire communities as the victims of environ-
mental harm, ar ising, for example, from the contamination of food and
water supplies. Financial compensation might then focus on payments
to those — including the public — who have suffered losses or incurred
expenses associated with remedying environmental damage or taking
measures to prevent the spread of such damage.1
1 For discuss ion of restoration, see Chapter 11.
ENVIRONMENTAL L AW
216
Many aspects of environmental damage as just discussed fall out-
side the scope of compensation as generally understood in the context
of tort claims. For purposes of comparison it is worthwhile to review
that approach prior to examining alternative approaches to environ-
mental losses:
Traditionally, the courts considered the only measure of compensa-
tion for damage to property to be the diminution in value caused by
the tortfeasor’s wrong, that is, the difference between the property
value before and after the occ urrence of damage. The cost of restoring
or repairing t he property, if considered at all, was simply regarded as
a means of determining the diminution of value. However, in many
cases, the distinction is irrelevant. Where the cost of restoration is
equal to or less than the diminution of capital value, the repair is
always recoverable, even if the plaintiff does not actually incur the
cost. Moreover, where the repairs fail to restore the property to its
original value, the plaintiff is entitled to the cost of repair and to an
additional sum to compensate for the residual def‌iciency. However,
where the cost of restoring the property is greater than the diminu-
tion of value the cases are divided as to which measure of damages
should be applied. Most case s follow the tradit ional approach so th at
the plaintiff is only entitled to damages suff‌icient to compensate for
a diminution of propert y value. However, damages wi ll be measured
according to the cost of repair if restoration alone will make good
the plaintiff’s loss . . . . The latter approach will only be adopted if
the plaintiff actually intends to effect repairs and if the cost of such
repairs is reasonable.2
As environmental losses are more fully appreciated in a context
that encompasses recognition of such principles as polluter pay, inter-
generational equity, and the values of biodiversity and ecological integ-
rity, attention has shifted from individualized claims to a more broadly
conceived framework for evaluating compensation. As seen in Brit-
ish Columbia v Canadian Forest Products Ltd3 (discussed later in this
chapter), the willingness of courts to explore new issues around the
valuation of environmental losses introduces methodological and evi-
dentiar y challenges.
2 LN Klar et al, R emedies in Tort, vol 4, loose-leaf (Toronto: Carswell, 1999–) at 27.
3 British Columbia v Cana dian Forest Products Ltd, 2004 SCC 38 [Canfor].

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