system would be $3.5 billion per year, which was nine times the cost of the cheaper version. In addition,
the EPA reserved the right to reduce standards for specific plants if they demonstrated that the costs of
compliance would be significantly greater than the benefits.
Riverkeeper, Inc. an environmental organization, challenged these regulations. The appeals court ruled
that the EPA could only consider costs in two circumstances: (1) determining if they could be ‘reasonably
borne’ by the industry or, (2) if there were two ways to achieve the same goal, the EPA could mandate the
cheaper option. The court said, however, that the EPA could not compare the costs and benefits of various
methods, and choose the technology with the best net benefits. Nor could the EPA alter standards for
specific sites based on cost-benefit analysis. The Supreme Court granted certiorari.
Issue: Is the EPA permitted to use cost-benefit analysis when issuing regulations?
Excerpts from Justice Scalia’s Decision:[The CWA] instructs the EPA to set standards for cooling water
intake structures that reflect “the best technology available for minimizing adverse environmental
impact.” The Second Circuit took that language to mean the technology that achieves the greatest
reduction in adverse environmental impacts at a cost that can reasonably be borne by the industry. That is
certainly a plausible interpretation of the statute. But “best technology” may also describe the technology
that most efficiently produces some good. In common parlance one could certainly use the phrase “best
technology” to refer to that which produces a good at the lowest per-unit cost, even if it produces a lesser
quantity of that good than other available technologies.
[Plaintiffs] contend that this latter reading is precluded by the statute’s use of the phrase “for minimizing
adverse environmental impact.” Minimizing, they argue, means reducing to the smallest amount possible,
and the “best technology available for minimizing adverse environmental impacts,” must be the
economically feasible technology that achieves the greatest possible reduction in environmental harm.
But “minimize” is a term that admits of degree and is not necessarily used to refer exclusively to the
“greatest possible reduction.” It seems to us, therefore, that the phrase “best technology available,” even
with the added specification “for minimizing adverse environmental impact,” does not unambiguously
preclude cost-benefit analysis.
[I]t was well within the bounds of reasonable interpretation for the EPA to conclude that cost-benefit
analysis is not categorically forbidden. In the requirements challenged here the EPA sought only to avoid
extreme disparities between costs and benefits. The agency limited variances from the national
performance standards to circumstances where the costs are significantly greater than the benefits of
compliance. And finally, the EPA’s assessment of the relatively meager financial benefits of the
regulations that it adopted–reduced impingement and entrainment of 1.4 billion aquatic organisms, with
annualized benefits of $83 million, when compared to annual costs of $389 million, demonstrates quite
clearly that the agency did not select the regulatory requirements because their benefits equaled their
costs.
While not conclusive, it surely tends to show that the EPA’s current practice is a reasonable and hence
legitimate exercise of its discretion to weigh benefits against costs. In the last analysis, even [plaintiffs]
ultimately recognize that some form of cost-benefit analysis is permissible. They acknowledge that the
statute’s language is “plainly not so constricted as to require EPA to require industry petitioners to spend
billions to save one more fish or plankton.” This concedes the principle–the permissibility of at least
some cost-benefit analysis–and we see no statutory basis for limiting its use to situations where the
benefits are de minimis rather than significantly disproportionate.
The judgment of the Court of Appeals is reversed.
Question: Is the EPA now allowed to use a cost-benefit analysis under the Clean Water Act?
Question: What would be the annual benefit cost?
Question: What would the annual costs be?
Question: Do the benefits of reducing the impingement and entrainment of 1.4 billion aquatic
organisms outweigh the costs?