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Criteria for Evaluating Environmental Policies

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Title: Criteria for Evaluating Environmental Policies


1
Criteria for Evaluating Environmental Policies
  • Field, chapter 9

2
Policy Criteria
  • In evaluating the effectiveness and
    appropriateness of a policy for addressing a
    given problem in environmental pollution control,
    it is important to have clearly in mind a set of
    policy evaluation criteria.

3
List
  • Their ability to achieve efficient and
    cost-effective reductions in pollution.
  • Their fairness.
  • The incentives they offer to people to search for
    better solutions.
  • Their enforceability.
  • The extent to which they agree with certain moral
    precepts.

4
EFFICIENCY
  • An efficient policy is where marginal abatement
    costs and marginal damages are equal.
  • One way of thinking about environmental policies
    is along a continuum from centralized to
    decentralized.
  • A centralized policy requires that some control
    administrative agency be responsible for
    determining what is to be done.

5
Measurement
  • To achieve efficiency in a centralized policy,
    the regulatory agency in charge must have
    knowledge of the relevant marginal abatement cost
    and marginal damage functions, then take steps to
    move the situation to the point where they are
    equal.
  • It is often the case that environmental damages
    cannot be measured accurately.

6
Cost Effectiveness
  • Measurement issues makes it useful to employ
    cost-effectiveness as a primary policy criterion.
  • A policy is cost-effective if it produces the
    maximum environmental improvement possible for
    the resources being expended or, equivalently, it
    achieves a given amount of environmental
    improvement at the least possible cost.
  • For a policy to be efficient it must be
    cost-effective, but not necessarily vice versa.

7
Less Abatement than Desired
  • If programs are not cost-effective,
    administrators will tend to set less restrictive
    targets in terms of desired amounts of emission
    reductions.
  • The real problem with having costs higher than
    they need to be is that society will be inclined
    to set its objectives too low in terms of the
    amount of emission reduction sought.

8
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9
FAIRNESS
  • Equity is, first and foremost, a matter of
    morality and the concerns about how the benefits
    and costs of environmental improvements ought to
    be distributed among members of society.
  • It has to be recognized that there is no
    agreement on how much weight should be put on the
    two objectives efficiency and distribution.

10
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11
Environmental Justice
  • The concern is that racial minorities and
    low-income people are disproportionately exposed
    to environmental contaminants, both those outside
    the home such as air and water pollution and
    those within the home and workplace such as lead.
  • Its possible that low-income households locate
    close to hazardous waste sites because property
    values are lower.

12
INCENTIVES FOR LONG-RUN IMPROVEMENTS
  • It is firms and consumers whose decisions
    actually determine the range and extent of
    environmental impacts.
  • The incentives facing these private parties
    determine how and where these impacts will be
    reduced.
  • Do environmental policies provide strong
    incentives for individuals and groups to find
    new, innovative ways of reducing their impacts on
    the environment?

13
Incentives for RD
  • Shifting downward the marginal abatement cost
    function makes it cheaper to secure reductions in
    emissions, because this will justify higher
    levels of environmental quality.

14
ENFORCEABILITY
  • There perhaps is a natural tendency among people
    to think that enacting a law automatically leads
    to the rectification of the problem to which it
    is addressed.
  • Among the environmental community this tendency
    is depressingly strong.
  • Enforcement requires energy and resources.
  • There will always be people whose interests lie
    in not having environmental policies enforced.

15
Compliance
  • The GAO once surveyed a large number of major
    wastewater dischargers in the country.
  • They found that a substantial fraction (more than
    one-third) of the sources were not in compliance.
  • RFF surveyed state enforcement agencies to
    determine common practices and costs associated
    with enforcing pollution-control regulations.
  • A widespread practice is for agencies to require
    self-reporting of emissions by firms.

16
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17
Enforcement
  • There are two main steps in enforcement
  • Monitoring refers to measuring the performance in
    comparison to whatever requirements are set out
    in the relevant law.
  • Sanctioning refers to the task of bringing to
    justice those whom monitoring has shown to be in
    violation of the law.
  • Authorities often seek to achieve voluntary
    compliance encouraging violators to remedy the
    situation w/o penalty.

18
Paradox
  • One might think that the greater the
    sanctionshigher fines, long jail terms for
    violators, and so onthe more the law would deter
    violators.
  • But the higher the penalties, the more reluctant
    courts may be to apply them.
  • The threat to close down violators, or even to
    levy stiff financial penalties, can in turn
    threaten the economic livelihoods of large
    numbers of people.

19
 MORAL CONSIDERATIONS
  • The innate feelings that people have about what
    is right and wrong affect the way they look at
    different environmental policies.
  • Take, for example, the question of choosing
    between effluent taxes and effluent subsidies.
  • Subsidies may be more effective.
  • Some people regard polluting behavior as
    essentially immoral.
  • Those who cause a problem ought to bear the major
    burden of alleviating it.

20
GOVERNMENT FAILURE
  • Government failure means that it cannot simply be
    assumed that each and every attempt at public
    environmental policy will make the situation
    better.
  • Government failure refers to systematic
    tendencies and incentives within legislatures and
    regulating agencies that work against the
    attainment of efficient and equitable public
    policy.
  • Outcomes in the political process may not
    resemble informed, rational public policy that
    advances the welfare of society.
  • The process could make the situation worse in
    some circumstances. (See Anderson, Political
    Environmentalism)

21
SUMMARY
  • Efficiency and cost-effectiveness
  • Equity
  • Incentives for long-run innovations
  • Enforceability
  • Agreement with moral precepts
  • Several traditional decentralized approaches, (ch
    10)
  • The use of standards, a centralized approach that
    has been the most frequently used historically
    (ch 11)
  • Incentive-based policies (chs 12-13)
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