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National Performance Measures Strategy
Testimony of Alexander Volokh
Policy Analyst, Reason Foundation
before the
U.S. Environmental Protection Agency's
Office of Enforcement and Compliance Assurance
San Francisco, Ca.
relating to the
National Performance Measures Strategy
March 17, 1997
My name is Alexander Volokh of the Reason Foundation, a public policy
research organization based in Los Angeles. I am also the co-author of
Environmental Enforcement: In Search of Both Effectiveness and
Fairness.�
Thank you for giving me the opportunity to speak to you about the National
Performance Measures Strategy.
I will offer some ideas for developing new performance measures, but we
cannot begin to reform the old system without precisely understanding its
failings. The problem with the old input-counting system was not that it
gave us wrong information, but that the information it gave us did not
help us to figure out whether the enforcement agency was doing a good job.
The main problems are the following:
1. First, the numbers that are reported are often meaningless, because
they
do not make important distinctions � such as distinctions between trivial
and harmful violations, accidental and intentional violations, and
violations taking place in different media.
2. Second, increasing numbers of enforcement actions are interpreted as
success, while in fact (even when the numbers are meaningful) this is not
necessarily the case.
Let me briefly discuss two sorts of problems with the current performance
measures.
1. What do the numbers mean?
Because not all violations are the same, aggregated numbers often mean
less than they seem.
a. Violations have different impacts.
A one-time permit exceedence involving a low-level, low-toxicity pollutant
in an uninhabited area is not the same as dumping a highly poisonous
chemical into the water supply near a major city. To say that "one trivial
violation + one harmful violation = 2" gives us no information on whether
the EPA is solving real problems.
b. Violations have different moral qualities.
Since the law is at least in part supposed to be a deterrent to bad actors
and a tool of moral education, we would like to concentrate our resources
on intentional and reckless violations. An accidental paperwork mistake is
not the same as intentionally defrauding the EPA or treating chemicals in
a way that one knows has a high chance of killing people. To say that "one
accidental violation + one intentional violation = 2" gives us no
information on whether the moral goals of the law are being properly
fulfilled.
c. The environment is multi-dimensional.
Suppose that by transferring resources from air to water enforcement, we
reduce air enforcement actions by 2 but increase water enforcement actions
by 1. The numbers would indicate that total enforcement actions have
decreased by 1. But counting total enforcement actions does not work here
either. An air quality violation is not equivalent to a water quality
violation, which is not equivalent to a taking of endangered species. In
allocating its enforcement resources, the EPA is implicitly making this
judgment. But there will always be a certain amount of arbitrariness in
the decision. To say that�"one RCRA violation + one FIFRA violation = 2"
gives us no information on whether �enforcement results,� in some absolute
sense, are increasing or decreasing.
d. Environmental quality is subjective.
Intimately related to this last point is that environmental quality is
subjective. "Environmental quality" has no rigorous definition. Some
people consider biodiversity to be the most important environmental issue;
other people care about human mortality rates; others care about
sustainability. Even though we know that not all "paperwork" violations
are trivial -- some are quite important, since the entire system depends
on honest and accurate reporting -- there is no clear way to rank a
paperwork violation, which represents the possibility of future harm,
against, say, an actual oil spill.
Any measure that tries to reduce the enforcement program to just a few
aggregated numbers cannot hope to capture the complexity of environmental
protection and enforcement. Knowing the size of penalties or the number of
enforcement actions does not help us.
2. What do increases in the numbers mean?
Even seeing the evolution of these numbers through time gives us
misleading information. Here are two problems related to the
interpretation of changes in enforcement quantity.
a. Any improvement in environmental compliance will make the numbers go
down.
When the measure of success is the quantity of enforcement, the agency�s
performance record is hurt by any improvement in the environment or in
compliance. The business community has a more cooperative attitude toward
enforcement today than it had in the 1970s. This makes the numbers go down
and makes the EPA look as though it is doing less. If regulations suddenly
become simpler, noncompliance will drop dramatically, and again, the EPA
will look bad; conversely, if a new regulatory program is enacted, the
numbers will suddenly increase, giving the illusion of greater
effectiveness.
Every time the EPA spends money on a compliance assistance program or on
an audit program, it is taking resources that could otherwise be used on
traditional enforcement, and using them instead to increase compliance. To
the extent that an audit or compliance assistance program succeeds, it
again makes enforcement numbers decrease, and gives the impression that
the EPA is doing a bad job.
b. Any shift to more difficult cases will tend to make the numbers go
down.
We all know that environmental law is complicated and highly technical. A
National Law Journal survey reported that about two-thirds of corporate
environmental attorneys believed that their companies had violated some
environmental law over the past year, largely because of uncertainty and
complexity. They also believed that full compliance with all local, state,
and federal environmental laws was impossible. This means that someone
looking for violations of environmental laws is likely to find them,
especially in statutory regimes characterized by elaborate permit and
record-keeping systems, like the Clean Water Act. When the numbers
increase, it could mean that the enforcers are doing their job, or it
could mean that they have shifted to those violations that are easiest to
find, which are not necessarily the most valuable ones. Decreases or
increases in enforcement or failure. If the numbers increase, it doing
their job properly; that is, that numbers could indicate either success
could mean that the enforcers are they are trying harder and catching more
people. Or it could mean that compliance has gone down -- in other words,
that the enforcers are not doing their job. Or it could mean that
enforcers are picking the easier cherries. Unfortunately, it is impossible
to tell by looking at the numbers.
3. What should be done?
Whatever measures EPA know what the numbers adopts, it must address these
problems. We should be able to mean, and we should be able to interpret
what changes in the numbers mean. I suggest the following steps.
1. First, we should abandon our reliance on the total number of cases, the
total number of enforcement actions, or the total amount of penalties.
Such numbers, because they do not distinguish between intentional and
unintentional or between harmful and less harmful, cannot tell us whether
we are doing a good job. We should only add comparable things. This means
that the enforcement measures should be substantially more disaggregated:
- by amount of harm -- separated into �paperwork violations, "harmless
permit exceedences," "harmful emissions," and the like;
- by level of intent -- separated into "accidental violations,"
"negligent violations," "reckless violations," and "intentional
violations";
- by medium or by regulatory regime -- separated, for instance, into
"Clean Air Act violations," "Clean Water Act violations," "RCRA
violations," and so on.
A report that avoids excessive aggregation would allow different observers
to look at the numbers, knowing that the cases counted in them are closer
to being truly comparable. It would not mislead readers into seeing trends
that may not really be there. For instance, separating cases by regulatory
regime would allow readers to see when cases increase or decrease because
of changes in regulations and not because of changes in enforcement
quality.
Naturally, having too many categories could become unwieldy, so the number
of categories needs to be kept manageable. Even disaggregated, every one
of these categories will contain dissimilar cases. For instance, the
"accidental violations" category will contain both harmful and harmless
violations. Ideally, within any category, violations should be weighted by
gravity -- either by how much harm was caused, how bad the defendant�s
state of mind was, or both. One possible way of doing this would be by
using the factors that the EPA already uses to calculate its gravity-based
penalties.
2. Second, the EPA should be able to take credit for improvements in
compliance. Violations found by regulated parties over the course of an
environmental audit, or as the result of a compliance assistance program,
and . reported to the environmental agency, should be credited toward the
enforcement agency�s accomplishments at least as much as if the agency had
found the violation itself and punished the violator (even though the EPA
would not be allowed to assess actual penalties).
3. Third, the EPA should be able to take credit for improvements in the
state of the environment. The EPA should track environmental quality and
report it together with traditional enforcement numbers as part of its
accomplishments report. Thus, if enforcement has gone down because the
environment has improved, the accomplishments report should reflect this
trend.
Of course, interpretation of these data can be complicated, so all reports
should also be accompanied by narrative. For instance, as we run into
decreasing marginal returns, improving the environment may become more and
more difficult as time goes by, so maintaining a given level of
environmental quality may indicate success. Environmental enforcement
agencies should not have to take the blame for the results of substantive
policy decisions made by legislatures.
As I have mentioned, the environment is multi-dimensional and subjective:
no one number can capture environmental quality. Environmental quality
measurements may have to be broken down by medium, by pollutant, by
geographical area, or by some combination of the above. This would be a
desirable development, as it would underscore the complexity of
environmental quality measurements. Different observers, with different
value judgments about what constitutes the environment and which
environmental variables are more important, should be able to come to
intelligent conclusions from reading enforcement and performance reports.
4. Fourth, the measures of the enforcement program should not only provide
useful information for the concerned reader, but should also be useful to
legislators trying to decide whether to increase or decrease the agency�s
budget, and to the EPA itself, when trying to decide how to allocate its
resources. But deciding how to allocate resources -- and even deciding
whether particular environmental improvements are worthwhile -- is
impossible without some consideration of cost. The EPA should make some
effort to incorporate enforcement costs, both to itself and to private
parties, into its report. These costs could take the form of cost per
life-year saved or some other meaningful economic measure.
5. Fifth, the "reinventing enforcement" effort could also use some help
from Congress. If we are interested in some sort of rational resource
allocation that relates somehow to environmental risk, harm, and intent,
and that is interested in getting the greatest amount of environmental
protection from each enforcement dollar, it does not help that Congress
has required the EPA to enact complicated and expensive requirements,
often unrelated to risk, that sometimes tie up the EPA in enforcement
actions that may not be worthwhile. Congress should take the opportunity
during the upcoming RCRA and Superfund reauthorizations, for instance, to
improve compliance and enforcement by simplifying its regulations.
Some groups have suggested that whatever the EPA does in developing better
enforcement measures, it should not increase the amount of classified
information that might help citizen groups sue companies that violate an
environmental law. The importance of citizen suits has been used as an
argument against extended audit privilege laws. I would suggest, however,
taking a different approach. The entire Performance Measures Strategy is
based on the realization that bad measurements lead to bad incentives,
which lead to environmental enforcement actions that are not always
justified or even useful. But today, we live in a world where citizen
groups can sue a company for an accidental, harmless violation of an
environmental law. We do not require citizen groups to have standing --
that is, particular, individualized harm -- to enforce environmental laws,
and we cannot hold them accountable for excessive enforcement in the way
that we can hold the EPA accountable. Therefore, if we are concerned about
wrong cases being brought by the government, we should be at least as
concerned about wrong cases being brought by private parties. The effect
of audit privilege laws on citizen suits should not distract us from the
need to develop meaningful incentives for environmental compliance.
This concludes my remarks. Thank you for your attention.
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