Title: Environment Policy and Public Expenditure
1Environment Policy and Public Expenditure
ANIL MARKANDYA WORLD BANK
- Public Expenditure Analysis and Management
- Washington DC
- January 12, 2004
2KEY QUESTIONS
- Why should the government be involved in
financing environment-related infrastructure? - How should this financing be organized?
- How should the role of the government be
evaluated? - What can we say about current performance in this
area in non-OECD countries?
3A. 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).
4Why 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.
5Why 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.
6B. 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?
7General 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).
8General 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.
9General 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.
10Central 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).
11Type 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.
12C. 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!
13Environmental 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.
14Fiscal 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.
15Management 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.
16D. 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
17Actual 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.
18Actual 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.
19Reality Check Ukraine Case Study
20In 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.
21Assessment of Environmental Effectiveness
22Environmental 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.
23Environmental 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.
24Environmental 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.
25Related Question on Environmental Effectiveness
Is Overall Environmental Expenditure on
Environmental Protection Adequate?
26Environmental 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
27Recommendations 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.
28Assessment of Fiscal Prudence
29Fiscal 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.
30Fiscal 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).
31Assessment of Management Efficiency
32Management 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.
33Management 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.
34Management 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
35Management 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.
36Management 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.
37Management 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.
38Management 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.
39Recommendations 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.
40Recommendations 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
41Recommendations 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
42Recommendations 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