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Environment Policy and Public Expenditure

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Title: Environment Policy and Public Expenditure


1
Environment Policy and Public Expenditure
ANIL MARKANDYA WORLD BANK
  • Public Expenditure Analysis and Management
  • Washington DC
  • January 12, 2004

2
KEY QUESTIONS
  1. Why should the government be involved in
    financing environment-related infrastructure?
  2. How should this financing be organized?
  3. How should the role of the government be
    evaluated?
  4. What can we say about current performance in this
    area in non-OECD countries?

3
A. Why should the government be involved?
  • The private sector will not provide enough to
    meet social objectives of e.g. the MDGs.
  • But why does the private sector not provide
    enough?
  • Social benefits cannot be captured by the private
    sector (externalities, social objectives)
  • Access to finance for such investment is limited
    in developing countries
  • Returns to such investment are lower than for
    other private sector investments
  • Industry cannot afford the required investment.
    (PPP cannot be applied in all cases).

4
Why should the government be involved?
  • But these reasons for low private sector
    involvement are not sufficient to justify state
    provision.
  • Externalities can be internalized via fiscal
    incentives
  • Access to funds can be facilitated by special
    financial agencies
  • The problem is that, in many developing and
    transition countries, these instruments are not
    adequately developed and take time.

5
Why should the government be involved?
  • Hence government financing should be seen as an
    evolving process, where direct provision declines
    over time and indirect instruments are used to
    increase private provision.
  • Smaller government share can be enhanced by
    increased leveraging of public funds.
  • Nevertheless, there will always be a core of
    financing that will be needed from the
    government, to cover management and regulation,
    protection of pure public goods (water sources on
    public land), and financial support for social
    objectives.

6
B. How should the role of the government be
organized?
  • Main issues are
  • Financing from general taxation versus earmarked
    funds.
  • Expenditure from central versus local budgets
  • Use of government department, specialized agency
    (e.g. environment fund, water agency), public
    utility?

7
General Versus Earmarked Funds
  • Case for earmarked funds is strongest when
  • Revenues are raised from charges levied on
    environmental services and used to provide the
    services (e.g. protection of water sources)
  • When an environmental charge that is
    environmentally and economically desirable can
    politically only be levied when revenues are
    earmarked.
  • In many cases pollution charge revenues are
    earmarked in OECD and developing countries (e.g.
    carbon levy, landfill taxes in the UK, EU).

8
General Versus Earmarked Funds
  • Case against earmarked funds is
  • They make fiscal discipline more difficult (i.e.
    control of overall spending). But note that
    earmarking is not the same as making the funds
    extra budgetary.
  • Allocative efficiency is less (spending on the
    environment is determined by revenues, not by the
    return on the investment relative to other
    investments.

9
General Versus Earmarked Funds
  • In general the case for having some earmarked
    funds for the environment is strong.
  • On grounds of linking spending on environmental
    services to payments made for those services.
  • On grounds that fiscal instruments such as taxes
    can only be levied successfully if they are
    earmarked.

10
Central Versus Local Budgets
  • If the revenues are to be closely connected to
    the expenditures (the benefit principle), local
    control of the spending is more desirable.
  • On the other hand if expenditures are to be based
    more closely to national priorities, central
    control is better.
  • In practice both are needed and a compromise has
    to be reached. Central budgets also tend to be
    used more cost effectively (see below).

11
Type of Institution
  • Budget institutions versus specialized
    institutions.
  • The budget institutions apply budgetary control
    rules, which are easier to track, and facilitate
    fiscal discipline and transparency.
  • Specialized institutions such as environmental
    funds are often found to have lower levels of
    transparency.
  • The cost effectiveness of budget institutions is
    considered to be higher but this should not be
    exaggerated some other bodies can also work
    effectively.

12
C. Evaluating the Role of the Government
  • The OECD has proposed a number of criteria for
    evaluating this role in the environmental area
  • Environmental Effectiveness
  • Fiscal Prudence
  • Management Efficiency
  • But all these are predicated on sound data
    collection, which remains a serious problem!

13
Environmental Effectiveness
  • Public funds should not be used for investments
    that would have been made anyway.
  • Nor should they be used when the same objectives
    can be achieved through policy reforms (e.g.
    removal of subsidies)
  • The program of expenditure should be clear,
    consistent and open to scrutiny.
  • The environmental objectives should be defined
    and monitored.
  • Cost effectiveness indicators should be used to
    design and monitor the program
  • The funds should be leveraged as much as
    possible.

14
Fiscal Prudence
  • All public funds (even if earmarked) should be
    subject to the same fiscal discipline.
  • Earmarked funds should be required to adopt
    allocation rules as close as possible to those
    for other funds.
  • Spending by environment funds is subject to
    control to avoid quasi fiscal deficit
  • Spending is subject to audit and transparent
    ex-post reporting
  • All revenue collection is only done by the same
    authority and national procurement rules apply to
    the environmental funds.

15
Management Efficiency
  • Expenditure program is governed by clear, written
    rules, is based on consultation with civil
    society and carried out by a body representing
    all key stakeholders.
  • Day to day management is undertaken by a separate
    technically competent body.
  • A sound project cycle is adopted, laying out how
    project are prepared, appraised and selected.
  • Communication policy ensures that all applicants
    have equal access to information on funding
    opportunities and equal opportunity to have their
    projects impartially reviewed on a merit basis.
    Those who prepare the projects do not appraise
    them.
  • Financial products used are based on capacity to
    manage the risks. Grants are the simplest,
    followed by subsidies, loans, loan guarantees
    etc.

16
D. Actual Experience With Environmental Finance
  • What do studies carried out by the Bank tell us
    about the actual experience in environmental
    finance?
  • Recent studies include
  • Dominican Republic
  • India
  • Ukraine

17
Actual Experience
  • First and foremost we have a real problem finding
    out what has actually been spent on the
    environment!
  • Public spending has to be analyzed in the wider
    context of all environmental spending as the
    public/private division is changing over time.
  • In Indian study private sector data were not
    available
  • In DR data only partial public spending data were
    available
  • In Ukraine public and private data were available
    but private spending looks too high.

18
Actual Experience
  • Given the problems of measurement it is difficult
    to assess the environmental effectiveness, fiscal
    prudence and management efficiency.
  • Both the DR and Indian studies could not make a
    real estimate of these factors, except in a few
    ad hoc cases.
  • In the Ukraine study a more detailed estimate of
    these effects was made.

19
Reality Check Ukraine Case Study
20
In Ukraine Background Data
  • At aggregate level, environmental expenditures
    have fallen from around US1 billion in 1996 to
    US600 million in 2000.
  • Total expenditure in 2000 as of GDP is
    comparable to other CEE and OECD countries, but
    share of investment in total is less. In OECD it
    averages 27 and is much higher in countries
    catching up (e.g. Portugal). In Ukraine it is
    22.
  • Budgetary resources amounted to US35 million in
    2000, making only 6 of total environmental
    expenditure. This is very low and much lower
    than in OECD countries and CEE countries.

21
Assessment of Environmental Effectiveness
22
Environmental Effectiveness
  • By and large public funds are being used for the
    environment where other funds are not available.
    Enterprises and utilities could not afford to
    make the investments on their own.
  • Other policies that achieve environmental targets
    are being pursued (e.g. pollution charges are
    being raised to make up for inflation, integrated
    permitting is being introduce) but more can be
    done w.r.t. compliance on environmental standards
    and on leveraging public funds.

23
Environmental Effectiveness
  • National environmental policy has not been
    formulated in terms of specific environmental
    targets against which one can measure
    achievement.
  • The policy statements are mostly declarative in
    nature and do not provide priorities within the
    broad goals.
  • There are some specific goals related to
    environmental policy articulated in the national
    and regional Environmental Programs.

24
Environmental Effectiveness
  • The biggest problem with all these programs
    under funding. They contain much more than can
    be funded and the actually implemented is
    mostly lt10.
  • There is no way of knowing whether programs
    actually implemented are the ones with the
    highest priority. Tendency is to start a large
    number of projects and programs then argue for
    funds to complete them. (a practice common in the
    Soviet Union).
  • The bulk of state spending is on water resources
    protection, This is broadly consistent with
    national priorities.

25
Related Question on Environmental Effectiveness
Is Overall Environmental Expenditure on
Environmental Protection Adequate?
26
Environmental Effectiveness
  • Data show that while overall level is consistent
    with other countries, public share is too low and
    investment share is too low.
  • Composition of environmental expenditure has
    important implications.
  • For example The low share of public expenditure
    means that not enough is being spent on public
    goods -- such as monitoring of environmental
    quality, and protection of nature reserves and
    forests. In transition countries the state also,
    rightly, supports investment in water supply and
    sewerage, in other key areas of infrastructure
    and in key industrial enterprises, on public good
    grounds

27
Recommendations on Environmental Effectiveness
  • Link priorities with specific environmental goals
    and outcomes
  • Link expenditures more closely to priorities
  • Increase overall public investment on the
    environment.
  • Increase flexibility in allocation between public
    investments at different levels.

28
Assessment of Fiscal Prudence
29
Fiscal Prudence
  • The level of prudence is good in that
  • Environmental expenditures do not contribute to
    macroeconomic problems
  • Environmental funds are subject to audits
  • Environmental charges are collected by national
    tax authorities
  • The same procurement rules apply for the
    environment funds as for other government
    spending.

30
Fiscal Prudence
  • The level of prudence is less good in that
  • Decisions on environment spending are not always
    made in a manner consistent with other areas of
    spending (but other areas of public spending are
    also not that clearly and transparently done).

31
Assessment of Management Efficiency
32
Management Efficiency
  • Ample evidence expenditures are not efficient in
    the sense of selecting the programs and projects
    with the highest net benefits or obtaining the
    maximum improvement in any physical indicator per
    dollar spent.
  • Assessing efficiency is not easy benefits,
    especially from better protection of natural
    resources are difficult to quantify. Also the
    use of cost effectiveness criteria, well
    established for investments in sectors such as
    health and education, are less so for the
    environment.
  • Nevertheless, tools and techniques for such
    assessments are increasingly becoming available
    and should be used in Ukraine.

33
Management Efficiency
  • Efficiency is of course not simply a matter of
    using CBA/CEA.
  • Are policies based on proper consultation?
  • Ukraine has a reasonable system of consultation
    in deciding its environmental programs but it can
    be improved.
  • Is it easy to track expenditures by category and
    know when a spending unit has not delivered or
    has overrun the cost?
  • The monitoring of environmental expenditures is
    quite weak and accountability, especially at the
    local level, needs to be strengthened.
  • Does the method of allocation prioritize items
    within a program, so that when funds are
    inadequate the highest priority items are
    included?
  • It does not.

34
Management Efficiency
  • Ukraines principal sources of public
    environmental expenditure state and local
    budgets, and special, earmarked environmental
    funds linked to revenue from pollution charges.
  • The contributions from the Environment Funds can
    be in the form of direct investments or grants on
    a matching basis. The system of environmental
    funds is extensive and includes over 1,600
    regional and local funds

35
Management Efficiency
  • The sheer number of these funds is clearly
    inefficient. On the other hand, local government
    control is valued since decisions about how to
    spend resources can be made closer to where
    environmental problems exist. Compromise is
    needed.
  • The income of the funds comes primarily from
    pollution charges on emissions of air, water and
    waste. The highest revenues collected were for
    air pollution while the greatest expenditures are
    on mitigating water pollution.

36
Management Efficiency
  • Data disaggregated by region show that compliance
    rates with charges and fines are lower in the
    regions where pollution is higher and in these
    same regions, fines are less likely to be imposed
    on firms.
  • In some regions, this may be an indication that
    where charges become too high, firms have more
    problems paying.
  • Most likely however, lack of payment is a result
    of corruption in the system. The empirical
    analysis is at least consistent with a picture
    where large firms lobby successfully for
    exemption, while smaller firms bribe tax
    officials or simply do not pay the charges.

37
Management Efficiency
  • The purpose of the pollution charges is not to
    reduce pollution given their low levels, they do
    not provide an incentive to make investments in
    environmental improvement.
  • Rather it is to raise revenue for environmental
    protection. Over the last five years or so, these
    charges, which were fixed in nominal terms, have
    had their real value eroded. Since there is a
    continued need to maintain this expenditure, and
    there is no other clear source of financing, some
    restitution of their real value is justified.

38
Management Efficiency
  • More generally, are Environmental Funds an
    important way to finance environmental
    expenditures? For the time being, yes.
  • To ensure a minimum level of funding for the
    environment, there is no alternative available
    now and the present system has some features to
    commend it.
  • The National Environment Fund does operate
    relatively effectively projects are properly
    processed and it is open to adopting better
    methods of appraisal. It can also act as a source
    pf leveraging of funds for pollution abatement,
    if appropriately designed and if banks see
    support by the Fund as an indication that the
    project is justified.
  • At the same time, there is a need to overhaul the
    system of local funds there are too many of
    them and to change the system of subsidization
    across regions.

39
Recommendations on Efficiency
  • In the longer term, however, the program of
    comprehensive public finance reforms that ends
    all earmarking and subjects all revenues to
    integration into the public finance system
    implies that the Environment Funds will be phased
    out. Some sunset provision is therefore
    needed.

40
Recommendations on Efficiency
  • Increase transparency and public disclosure
  • Consider introducing international expenditure
    standards to better monitor environmental
    expenditures
  • Enhance accountability
  • Introduce economic appraisal techniques for
    environmental projects and programs

41
Recommendations on Efficiency
  • Refine the institutional and legal structure for
    environmental funds
  • Reduce the number of funds
  • Spend resources close to where they collected
  • Introduce more rigorous guidelines for use of
    funds
  • Introduce more rigorous guidelines for use of
    funds
  • Evaluate the success of funds with respect to
    outcomes

42
Recommendations on Efficiency
  • Phase out Environment Funds in the Long Run
  • Increase pollution charges to make up for some of
    the lost value due to inflation (400 since 1996)
  • Eliminate exemptions
  • Streamline the pollution tax structure (jump at
    Max. allowable emissions is too sharp).
  • Strengthen oversight to reduce corruption
  • Reduce charges if most enterprises in a region
    cannot pay
  • Simplify pollution tax procedures
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