diminishing and negative welfare returns of economic growth: an index of sustainable economic...
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Ecological Economics
ANALYSIS
Diminishing and negative welfare returns of economic growth: an
index of sustainable economic welfare (ISEW) for Thailand
Matthew Clarkea,*, Sardar M.N. Islamb
aSchool of Social Science and Planning, RMIT University, G.P.O. Box 2476V, Melbourne, Victoria 3001, AustraliabCentre for Strategic Economic Studies, Victoria University, P.O. Box 14428, Melbourne City MC, Victoria 8001, Australia
Received 19 March 2003; received in revised form 7 July 2004; accepted 25 October 2004
Available online 3 February 2005
Abstract
Thailand has achieved remarkable levels of economic growth over the last three decades. This sustained economic growth
has played a major role in reducing absolute poverty levels from nearly one third of the population in 1975 to presently less than
10%, thus increasing the welfare of many Thais. This performance ranks Thailand as one of the world’s most successful
economies during this period. However, an increasing number of studies have begun to find that at a certain point achieving
economic growth stops improving welfare and actually begins to diminish it due to the hidden and traditionally unreported costs
of associated with this growth. With one exception, these new studies have focussed on high-income countries. This study will
estimate an index of sustainable economic welfare (ISEW) for a developing country, Thailand, over a 25-year period, 1975–
1999. This paper concludes that even low–middle income countries are beginning to approach the point in which economic
growth produces both diminishing and, at times, negative welfare returns as the costs of achieving economic growth begin to
outweigh the benefits. These results are important for policy makers and highlight the importance of implementing alternative
welfare enhancing interventions that must be considered in place of simply achieving economic growth. The emphasis of this
paper is not on the methodology of estimating the ISEW for Thailand, but rather on the policy implications for developing
countries of diminishing and negative welfare returns brought about through the achievement of economic growth.
D 2004 Elsevier B.V. All rights reserved.
Keywords: Economic growth; Thailand; ISEW; Welfare
1. Introduction
Thailand has achieved remarkable economic
growth over the last three decades. This sustained
0921-8009/$ - see front matter D 2004 Elsevier B.V. All rights reserved.
doi:10.1016/j.ecolecon.2004.10.003
* Corresponding author. Tel.: +61 3 9925 2960; fax: +61 3 9925
1010.
E-mail address: [email protected] (M. Clarke).
economic growth has played a major role in reducing
absolute poverty levels from nearly one third of the
population in 1975 to presently less than 10% (Warr,
2001). This performance ranks Thailand as one of the
world’s most successful economies during this period.
As it is widely accepted within mainstream literature
that economic growth is a proxy indicator for welfare
(Pigou, 1962; Hicks, 1940; Ravallion, 2001), this 30-
54 (2005) 81–93
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–9382
year period of high economic growth indicates that the
welfare of all Thais has also significantly increased
during this time.
However, if welfare is not simply a function of
economic growth, but takes into account various
other issues such as inequality, environmental degra-
dation and sustainability, achieving economic growth
may in fact diminish welfare (Daly and Cobb, 1990).
An alternative index of welfare, the index of
sustainable economic welfare (ISEW), reflects this
new approach.
A number of ISEW studies have questioned the
relationship between economic growth and welfare
(Daly and Cobb, 1990; Diefenbacher, 1994; Hamil-
ton, 1998; Jackson and Marks, 1994; Lawn and
Sanders, 1997; Rosenberg and Oegema, 1995; Stock-
hammer et al., 1997). With only one exception
(Castaneda, 1999), each of these studies has focussed
on high-income countries. The constant finding across
all of these ISEW studies is that at a certain point,
additional economic growth reduces welfare.
Thailand is a worthwhile country to study because
as a high growth economy, it is often presented as a
model for other developing countries to imitate
(Watkins, 1998). It is important to apply the ISEW
to developing countries to investigate whether it is
possible for such low-income countries to prema-
turely reach this point whereby achieving economic
growth no longer increases economic welfare but
reduces it.
This paper will estimate an ISEW for Thailand
over a 25-year period, 1975–1999. This paper con-
cludes that Thailand, a low–middle income country, is
beginning to approach the point in which economic
growth produces both diminishing and, at times,
negative welfare returns as the costs of achieving
economic growth begin to outweigh the associated
benefits. This conclusion is important for policy
makers and highlights the importance of implement-
ing alternative welfare enhancing interventions in
place of simply achieving economic growth.
The emphasis of this paper is not the methodology
of the estimation of the ISEW for Thailand, as this can
be found elsewhere (Clarke and Islam, 2004), but
rather on the policy implications for developing
countries of diminishing and negative welfare returns
brought about through the achievement of economic
growth.
This study is divided into fix sections. This first
section introduces the paper. The following section
will set out the problem being considered. Section 3
will focus on the application of the ISEW to Thailand.
Section 4 will present the results. Section 5 discusses
the policy implications of these results. Conclusions
are drawn in Section 6.
2. Research problem
Achieving economic growth has been the central
theme of economic policy in most economies since
the end of the Second World War (Nordhaus and
Tobin, 1973; Manning, 2001). Governments in both
developing and developed countries are continuously
instigating policies designed to achieve economic
growth (see NESDB, 1996, 2000). There is little
doubt that the main purpose of increasing economic
activity is to increase welfare (Samuelson et al., 1978;
Kaosa-ard, 2000). Thus, the pursuit of economic
growth appears to be intimately tied with pursuing
increased welfare. The major question underlying the
ISEW approach is whether an increase in economic
growth dreally reflects the true changes in welfareT(Brekke, 1997, p. 158).
Sametz (1968) called for the costs and benefits of
changes in environment, leisure time, new products,
non-marketed goods, urbanisation, and government
expenditure caused by achieving economic growth to
be considered when measuring welfare. Nordhaus and
Tobin (1973) empirically applied this approach to the
United States and concluded that despite various
adjustments to GDP per capita, economic growth still
indicated improvements in welfare.
Daly and Cobb (1990) developed the ISEW
approach to question Nordhaus and Tobin’s (1973)
analysis and assumption that economic growth
automatically increases welfare. However, whilst this
new approach questioned the desirability of eco-
nomic growth, it was considered extremely unlikely
that economic growth would always be undesirable
with respect to welfare. It was acknowledged that
economic growth had a positive role to play in
enhancing welfare, but whether this would always
remain the case was of particular interest. The
relationship between economic growth and welfare
may include aspects of diminishing and negative
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–93 83
returns so that at a particular point in time, economic
growth no longer adds to welfare but actually reduces
it (Manning, 2001).
This point, in which economic growths ceases to
add to welfare and begins to reduce it, has been
labeled the Threshold Point (Max-Neef, 1991). The
consideration of such a point is not new within the
literature (Hicks, 1940; Pigou, 1962; Ng and Ng,
2001). For the past three decades, a number of
authors have argued that this point has been crossed
by developed countries (see Daly, 1971, 2000;
Barkley and Seckler, 1972; Zolotas, 1981; Hamilton,
1998). Thus, whilst the developed world has reached
an age of mass-consumption, welfare may have
decreased despite continuous increases in economic
growth. Social, political and environmental pressures
such as pollution, urbanisation, poorer health, and so
on, may have resulted in reduced levels of welfare
(Daly, 2000).
Consideration within this paper is given to whether
the dthreshold pointT be reached only by a so-called
wealthy society?T (Max-Neef, 1995, p. 117), or
whether it can also be reached by poorer countries
Economic sub-system
Spiritual sub-system
Social susystem
Ecologicalsystem
Fig. 1. Representation of interco
at much lower levels of economic development. The
answer may influence future development plans and
policies. Expectations for improving society’s welfare
through continuous economic growth would need to
be re-examined, as would the economic and social
policies for achieving this outcome.
3. Thailand and the ISEW
Castaneda (1999) summarised the findings of
previous ISEW studies (Daly and Cobb, 1990; Die-
fenbacher, 1994; Hamilton, 1998; Jackson and Marks,
1994; Lawn and Sanders, 1997; Rosenberg and
Oegema, 1995; Stockhammer et al., 1997). In general,
these studies (of developed countries) found that
welfare increased in line with economic growth
(though at a slower rate) until the late 1970s or early
1980s, at which time the ISEW began to fall despite
continuing increases in economic growth. The con-
clusion of these studies was that at a certain point, the
costs of achieving economic growth begin to out-
weigh the associated benefits resulting in falling
Political sub-system
b-
Environmental sub-system
parent
nnected systems analysis.
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–9384
welfare. At this point, (the threshold point), further
economic growth reduces welfare. The policy impli-
cations are significant as they challenge the under-
lying tenants of mainstream economics, that economic
growth is both central and fundamental for improving
welfare.
The value of Castaneda (1999) and this paper is
that the focus is on developing countries (Chile and
Thailand respectively). These countries are character-
ised by low-income levels, high underemployment,
political instability and poor social capital. Economic
growth is expected to remedy these ills. However, if
Table 1
Summary of adjustments for Thai ISEW
Item Positive/negative Rationale
Personal Consumption Basis of ISEW
Income Inequality Accounting for inequalit
Adjusted Personal
Consumption
Adjusted base for index
Public Expenditure
on Education
Positive Adding in non-defensive
expenses
Public Expenditure
on Health
Positive Adding in non-defensive
expenses
Commuting Negative Subtracting costs for tim
Urbanisation Negative Subtracted for defensive
private expenditure
Private Expenditure
on Health
Negative Subtracted for defensive
private expenditure
Public Expenditure
on Roads
Positive Accounting for services
included in public expen
Consumer Durables Positive Accounting for services
included in public expen
Corruption Negative Subtracting for unaccoun
political costs to society
Debt Negative Subtracting for unaccoun
political costs to society
Air Pollution Negative Subtracting costs of
environmental damage
Water Pollution Negative Subtracting costs of
environmental damage
Noise Pollution Negative Subtracting costs of
environmental damage
Deforestation Negative Subtracting costs of
environmental damage
Long Term Environmental
Damage
Negative Subtracting costs of
environmental damage
Commercial Sex Work Negative Unaccounted costs to
spiritual system
countries with low national income levels can reach a
threshold point and economic growth has diminishing
and negative welfare returns, whole new approaches
to development economics are required.
3.1. Systems analysis
Adjusting measures of national income to incor-
porate the unreported costs (and benefits) of achiev-
ing economic growth is based on an implicit premise
that the economy is part of a larger interrelating
system (Clarke, 2004). Assuming that society is
Methodology
From Thai National Statistics Office (NSO) (1997, 1999)
y Equally distributed equivalent level of income Atkinson’s
(1970)
75% of public expenditure on education due to low base
(NSO, 1997, 1999).
75% of public expenditure on health due to low base
(NSO, 1997, 1999).
e lost US$219 per car calculated in 1990 extrapolated to cover
all years (Tanaborrboon, 1990)
18% of Bangkok personal income is spent for access to
clean water and air (World Bank, 1999)
50% of all private health expenditure (Cobb and Cobb,
1994; NSO, 1997, 1999)
not
diture
50% of all public expenditure on roads (Daly and Cobb,
1990; NSO, 1997, 1999)
not
diture
10% of expenditure on cprivate consumer durables
(Daly and Cobb, 1990; NSO, 1997, 1999)
ted 0.0088% of GDP (1975–1981), 0.0074% of GDP
(1982–1988), 0.007% of GDP (1989–1999) based on
Phongpaichit and Piriyarangsan (1994)
ted 50% of interest paid on public Debt (NSO, 1997, 1999)
Costs of pollution abatement for Co2, CO, NOX, SOX,
SPM (Guenno and Tiezzi, 1998; Dept of EDP, 1990).
Costs of cleaning water is 7.5 baht per kilogram of
Biochemical Oxygen Demand (BOD) (Phansawas et al.,
1987; TESCO, 1993; Dept of IW, 1986)
1% of GNP (Daly and Cobb, 1990; NSO, 1997, 1999)
886 baht per hectare of forest lost is cost of soil erosion
(Panayotou and Parasuk, 1990)
Estimated damage for each tonne of carbon emissions is
21.59 baht (Nordhaus, 1991; Dixon, 1999)
3% of GNP (Phongpaichit et al., 1998; NSO, 1997, 1999)
Table 2
Summary of calculations—ISEW for Thailand
Income Distribution (cost) I ¼ 1�Pn
i¼1ðyi=lÞ1=1�a ap1
Public Education (benefit) Ed=PE(0.75)
Public Health (benefit) H=PH (0.75)
Commuting (cost) C=NRC(219d XR)
Urbanisation (cost) U=BY(0.08)+BY(0.1)
Private Health (cost) H(p)=PrHe(.05)
Public Roads (benefit) R=Pr(.05)
Consumer Durables
(benefit)
CD=Cd(0.1)
Corruption (cost) C(pol)=GDP1975–81(0.0088)+
GDP1982–88(0.0074)+
GDP1989–99(0.007)
Public Debt (cost) D(p)=IPD(0.5)
Air Pollution (cost) A=cCO2+cCO+cNOX+cSOX+cSPM
Water Pollution (cost) W=[(7.5�IP)+(7.5�4.6�MP)]�2
Noise Pollution (cost) N=GDP(0.01)
Deforestation (cost) D=DF(886)
Long-term Environmental L=cCDt+cCWRt+cCFt
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–93 85
systems-based underscores the need to consider the
wider welfare implications of achieving economic
growth. Within this application of the ISEW to
Thailand, explicit systems analysis is undertaken.
Society is made up of hierarchical and intercon-
nected systems and sub-systems (Capra, 1982;
Dopfer, 1979; Clayton and Radcliffe, 1996; Islam
et al., 2003). Within this approach, the ecological
system is considered the parent system and the social
sub-systems are the economic, social, environment,
political and spiritual (see Fig. 1). Each of these sub-
systems has a direct impact on society’s well-being
and therefore, measures of welfare must take into
account each of these sub-systems in order for that
measure to be accurate.
The following adjustments that explicitly recognize
the impact of achieving economic growth on various
sub-systems should be undertaken in estimating an
ISEW for Thailand (other adjustments might be
necessary for other countries) in order to measure
changes in welfare.
Damage (cost)Commercial Sex Work
(cost)
CSW=GNP (0.3)
where: I=measure of income inequality; yi=income of individuals in
the ith income range; l=mean income; a=society’s perspective on
equality; Ed=benefits of public education; PE=expenditure on public
education; H=benefits of public health care; PH=expenditure on
public health care;C=cost of commuting; NRC=number of registered
cars in Bangkok; XR=exchange rate; U=cost of urbanisation;
BY=average income for Bangkok residents; H(p)=cost of private
health care; PrHe=expenditure on private health care; R=benefits of
public roads; Pr=expenditure on public roads; CD=benefits of
consumer durables; Cd=expenditure on consumer durables; C(pol)=
costs of political corruption; GDP=gross domestic product;
D(p)=cost of public debt; IDP=interest paid on public debt A=cost
of air pollution; cCO2=cost of carbon dioxide (.03335 baht per
kilogram); cCO=cost of carbon monoxide (.03335 baht per kilo-
gram); cNOX=cost of nitrogen monoxide (2.84 baht per kilogram);
cSOX=cost of sulfur monoxide (7.4 baht per kilogram); cSPM=cost
of suspended particulate matters (4.15 baht per kilogram);W=cost of
water pollution; IP=industrial pollution, =FI+DI+PI+CI+TI; FI=food
industry BOD; DI=drink industry BOD; PI=paper industry BOD;
CI=chemical industry BOD; TI=textile industry BOD; MP=munici-
pal population BOD; BOD=biochemical oxygen demand; N=cost of
noise pollution; GDP=gross domestic product; D=cost of deforesta-
tion; DF=hectares of deforestation; L=cost of long-term environ-
mental damage; cCDt=cost of carbon emissions of deforestation,
=21.59�tonne of carbon emission; cCWRt=cost of carbon emissions
of wet rice farming, =21.59�tonne of carbon emission; cCFt=cost of
carbon emissions of fuel consumption, =21.59�tonne of carbon
emission; CSW=cost of commercial sex work industry; GNP=gross
national income.
Economic sub-system
! Personal consumption adjusted for income
inequality
Social sub-system
! Public expenditure on education
! Public expenditure on health
! Private expenditure on health
! Urbanisation! Commuting
Political sub-system
! Government streets and highways
! Consumer durables
! Corruption! Debt
Environmental sub-system
! Air pollution! Water pollution
! Noise pollution
! Loss of forests! Non-renewable resources
! Long-term environmental damages
Spiritual sub-system
! Commercial sex work
As these sub-systems inter-relate, some adjust-
ments may cross-over various components (i.e.
commuting could be considered an adjustment for
social, political, environmental and even spiritual sub-
systems—sitting in a traffic jam provides a wonderful
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–9386
chance to contemplate the meaning of the universe
and its conspiracy against you!). However, for
simplicity (and to avoid double counting), it is of
interest to categorise the adjustments within only one
sub-system (Tables 1 and 2).
3.2. Adjustments unique to the Thai ISEW
The methodology for estimating the separate costs
and benefits can be found elsewhere (Clarke and
Islam, 2004). In general, the methodology has
followed that set out previously (Daly and Cobb,
1990; Cobb and Cobb, 1994). However, a small
number of adjustments within this ISEW have not
been made in previous ISEW studies. The Thai-
specific adjustments are corruption, debt and com-
mercial sex work. The decision to include these
adjustments within the Thai-ISEW is justified by
accepting the principles of normative social choice
theory (Bonner, 1986; Islam, 2001; Clarke and Islam,
2004).
Table 3
ISEW per capita and GDP per capita for Thailand, 1975–1999 (1988 pric
Year Economic
(millions
of baht)
Social
(millions
of baht)
Political
(millions
of baht)
Environmenta
(millions of ba
1975 289,271 �14,226 �3336 �81,373
1976 309,968 �14,380 �2771 �80,580
1977 333,312 �17,629 �5263 �137,464
1978 348,689 �17,828 �4460 �145,862
1979 368,041 �17,613 �5865 �70,782
1980 386,847 �16,607 �7034 �75,363
1981 405,849 �20,549 �8540 �79,451
1982 408,616 �17,597 �10,231 �83,773
1983 432,608 �17,658 �11,473 �83,698
1984 438,488 �21,985 �13,914 �87,772
1985 439,241 �25,719 �15,881 �90,177
1986 447,554 �28,279 �18,989 �74,774
1987 483,945 �35,342 �17,922 �78,871
1988 521,801 �43,117 �17,445 �85,397
1989 552,434 �48,866 �16,382 �91,478
1990 603,071 �54,663 �10,593 �113,112
1991 622,392 �60,523 �7050 �120,985
1992 655,585 �63,159 �2937 �126,737
1993 719,644 �57,618 781 �134,028
1994 785,056 �57,295 3409 �141,474
1995 853,737 �59,299 8159 �150,382
1996 929,336 �66,005 10,343 �158,653
1997 932,210 �65,835 2765 �163,368
1998 830,688 �55,185 �292 �163,192
1999 832,001 �70,019 �7335 �148,076
Normative social choice refers to the processes of
ordering alternative social states on the basis of the
choices, preferences and value judgments of members
of that society to determine what is the best state for
that society. Normative social choice theory incorpo-
rates the various social concerns around welfare that
are not adequately captured using individual prefer-
ence satisfaction techniques within the market place.
Normative social choices can be estimated using
expert opinion (or analyst), government formulated
public policy, or specific interviews of individuals on
welfare outcomes. The methodology for each techni-
que is well established (Islam, 2001). Using one, or a
combination of the above, it is possible to determine
the social choice perspectives on various welfare
issues. While not unique to Thailand, corruption, debt
and commercial sex work are all issues (identified by
experts, government policy or social research) that
reduce welfare in Thailand (Phongpaichit and Piriyar-
angsan, 1994; Phongpaichit et al., 1998; World Bank,
2000).
es)
l
ht)
Spiritual
(millions
of baht)
ISEW
(millions
of baht)
ISEW
per capita
GDP
per capita
�18,646 171,690 4050 14,662
�20,371 191,866 4440 15,754
�22,430 150,526 3400 16,942
�24,558 155,981 3449 18,237
�25,744 248,037 5379 18,819
�27,190 260,653 5550 19,458
�28,562 268,747 5614 20,206
�30,133 266,882 5464 20,883
�32,043 287,736 5811 21,729
�33,754 281,063 5556 22,504
�35,137 272,327 5258 22,996
�36,950 288,562 5448 23,722
�40,599 311,211 5777 25,561
�46,051 329,791 6000 28,380
�51,838 343,870 6153 31,316
�57,650 367,053 6519 34,565
�62,420 371,414 6520 37,073
�66,967 395,785 6849 39,506
�72,808 455,971 7816 42,765
�79,645 510,051 8631 45,174
�86,771 565,444 9510 48,511
�91,513 623,508 10,372 51,489
�89,590 616,182 10,132 49,691
�79,414 532,605 8665 45,348
�82,165 524,406 8505 45,789
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–93 87
4. Results
Both the level and trend of welfare differs when
measured by movements in ISEW per capita or gross
domestic product (GDP) per capita indices. The ISEW
per capita increases at a slower rate, but is also
decreases at times when GDP per capita is actually
increasing (i.e. at times of economic growth). The
ISEW per capita rose and fell throughout the 1980s,
effectively being unchanged in 1986 from the 1979
figure. In comparison, GDP per capita rose over 25%
over this same period (Table 3).
The ISEW per capita rose steadily during the next
decade though at significantly different rates than the
GDP per capita. Within this period, the divergence
between the two indices becomes quite apparent
(Fig. 2).
Both indices peak in 1996. This is just prior to
the financial crisis of 1997. After 1996 both indices
begin to fall. Whilst GDP per capita has shown the
propensity to increase in 1999, ISEW per capita
has not increased but has fallen again. It is too
early to confirm whether this is a trend or a
fluctuation. However, by drawing on the results of
other studies (Daly and Cobb, 1990; Jackson and
Marks, 1994), a continuing of this divergence could
be expected.
0
10000
20000
30000
40000
50000
60000
1975
1976
1977
1978
1979
1980
1981
1982
1983
1984
1985
1986
1987
ISEW per capita (1988 prices
Fig. 2. Comparison of ISEW per capita and GDP per capita me
It is important to note that even though both the
ISEW per capita and GDP per capita welfare indices
are money-metric, they should be considered ordinal
rather than cardinal. It is therefore incorrect to say that
if ISEW per capita (or GDP per capita) increases 10%,
welfare also increases 10%. Further, it is also not
accurate, when comparing the levels of GDP per
capita and ISEW per capita to infer that the money-
metric difference between these two indices (i.e. in
1988 GDP per capita is 28380 baht while ISEW per
capita is 6000 baht, a difference of 22380 baht) is the
difference in welfare. What can be inferred from these
two time series though is the variation and divergence
in the two trend lines. The analysis of the welfare
experienced by the Thai population between 1975 and
1999 is, in this instance, dependent on the shape of
these two trend lines.
The trend line for GDP per capita has three main
phases; the initial steady rise to 1986, the accelerated
growth to 1997 and the final dip and apparent
recovery to 1999. However the pattern for ISEW per
capita is significantly different. The rise is slower,
there is not an accelerated period, nor is there an
indication of a recovery in the final year after the
index begins falling in 1997. Comparing the two
indices further, an increasing divergence is also
apparent. This indicates that the relationship between
1988
1989
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
) GDP per capita (1988 prices)
asures of welfare for Thailand, 1975–1999 (1988 prices).
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–9388
GDP per capita and ISEW per capita is becoming
increasingly weaker throughout the time series,
casting doubts over the long-term desirability of
economic growth in Thailand in terms of welfare.
This is also illustrated by comparing the two
measures as indices with a base year of 1975. The
GDP per capita index maintains its three phases of
growth (constant, accelerated and crisis), whilst the
ISEW per capita index rises and falls through to the
earlier 1990s, then has a steady period of growth
before falling again following the financial crisis in
1997 (Fig. 3).
The most significant adjustment in this ISEW was
the cost of inequality to welfare. This was eight times
more important than the estimated costs of commer-
cial sex work. The largest positive adjustment within
the ISEW was education.
Studies suggesting that achieving economic growth
may decrease a nation’s aggregate welfare are limited
within mainstream literature. When discussed, such
economic growth has been termed impoverishing, or
welfare-reducing (see Ng and Ng, 2001). However,
these descriptions are limited as they do not
adequately describe Thailand’s experience in which
0
50
100
150
200
250
300
350
400
1975
1976
1977
1978
1979
1980
1981
1982
1983
1984
1985
1986
1987
ISEW p.c. for Thailand (1975 = 100) GDP
Fig. 3. Comparison of ISEW per capita and G
welfare levels improve by increasingly diminishing
rates due to the increasing costs of achieving
economic growth compared to the associated benefits.
The concept introduced is stunting economic growth.
This phenomena is so-called because this economic
growth has bretarded the progressQ of welfare. Duringperiods of stunting economic growth, welfare
improves at decreasing rates, remains stagnant, and
at times (while continuing to trend upwards) falls.
Stunting economic growth is undesirable as its effects
are sub-optimal. Optimal economic growth results in
welfare increasing at the maximum rate. However,
when the associated costs and benefits of achieving
economic growth are considered, it can be seen that
welfare does not always increase at the maximum rate.
Thus, at these times, economic growth is sub-optimal
or stunting in terms of welfare. This conclusion is in
line with other work, such as Thailand’s performance
in the Human Development Index (UNDP, 2002).
However, further ISEW studies for other developing
countries is required before conclusions can be drawn
on the generality of the Thai economic growth
experience and how this might compare to the
economic growth experience of other poor countries.
1988
1989
1990
1991
1992
1993
1994
1995
1996
1997
1998
1999
+Sheet1!$25:$25p.c. for Thailand (1975 = 100)
DP per capita for Thailand, 1975=100.
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–93 89
5. Policy implications
It is reasonable to base policy initiatives on
welfare indices (Hagerty et al., 2001). Before doing
so however, it is prescient to discuss the current
debate on the merit of the ISEW approach for this
purpose. Neumayer (1999, in press) argues that due
to a number of weaknesses, the ISEW is a faulty
measure of welfare. His reservations include the
question of weighting, bias in composition, theoret-
ical weaknesses in methodology and the merging of
sustainability and welfare into one measure. Lawn
(2003) has defended the ISEW in terms of both its
theoretical underpinnings and its composition. Lawn
(in press) has also further called for a standardized
ISEW to be developed with a common set of
methodologies in order to dampen this specific
criticism. As Daly and Cobb (1990) set out, the
initial purpose of the ISEW approach was to widen
the scope of debate around welfare in order to move
beyond an all-encompassing focus on achieving
economic growth (also see the justifications for
the Human Development Index; UNDP, 1990). In
this regard, Nuemayer’s criticisms should be con-
sidered important but not sufficient reason to cease
analysis.
Perhaps in part due to this ongoing debate, policy
implications based on the analysis of ISEW are rare
within the literature, especially for developing coun-
tries. Therefore, having reviewed the results of the
ISEW, it is important to discuss policy perspectives
that logically follow from this welfare economic
analysis. These are not policy prescriptions but rather
are issues that should be considered by those
determining policies.
5.1. Reduce emphasis on economic growth
Economic growth is not always desirable with
regards to increasing welfare as its net benefits are
sometimes negative and rarely as positive as unad-
justed aggregated standard national accounts growth
rates would suggest. Therefore, the first policy
suggestion is to reduce the emphasis on resource
consumption based economic growth. For example,
see the welfare costs within the Thai ISEW of
deforestation caused through achieving economic
growth.
A balanced approach to achieving economic
growth is required. Economic growth should not be
the only priority within government policies. Eco-
nomic growth aimed at specific sectoral areas (Warr,
2001) and for specific purposes would be better
drather than pursuing economic growth for its own
sake and hoping that the benefits will be spread
widely enough that the poor derive some gainsT(Fields, 1995, p. 76).
5.2. Emphasise pro-poor policies
Pro-poor policies are required to ensure that the
poor receive the benefits of any future economic
growth or any residual benefits from previous growth.
If economic growth is pursued, one of its specific
purposes must be to reduce poverty. Within Thailand,
the Northeast region has traditionally been the poorest
region, having poverty rates similar to parts of sub-
Saharan Africa (Watkins, 1998). Whilst economic
growth has been extremely high, the majority of the
population who remain rural have been largely
unaffected by its direct benefits but have experienced
its associated costs (Dixon, 1999; Warr, 2001). Whilst
controversial, a pro-poor policy that should be consid-
ered is income redistribution. (Inequality is the largest
cost to welfare associated with economic growth
within the Thai ISEW). Whilst there are attendant
costs with re-distribution (Pigou, 1962), it is more
likely to reduce income inequality than simple eco-
nomic growth. Such redistribution though is not
undertaken to increase prospects for future growth
(Chenery et al., 1974), but rather for the expressed
purposes of reducing poverty and hence lifting welfare.
The reduction of inequality reduces the poverty
elasticity so future growth has a greater impact on
reducing poverty levels (World Bank, 2000; Deolali-
kar, 2002). The reduction of inequality also encourages
social inclusion (Killock, 2002; Maxwell, 2001, 2003;
McKay, 2002; White, 2000). Whilst poverty levels
have decreased (Kakwani and Krongkaew, 2000), a
large absolute number of Thais are still struggling to
survive despite three decades of remarkable growth.
5.3. Emphasise other sub-systems
By defining and measuring welfare using systems
analysis, the importance of non-economic sub-systems
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–9390
has become apparent. Public policies can emphasise
the impact other domains have to increase welfare.
There are three main environmental policy areas
that would positively impact welfare levels: (1)
natural resource protection; (2) pollution control and
abatement programs; and (3) limits on harvesting
renewable resources. Whilst such government policies
might exist, they may not be adequately enforced. Re-
emphasising these policy areas is therefore important.
The costs within the Thai ISEW of pollution and
environmental degradation caused through achieving
economic growth are quite significant.
Thailand has suffered a significant decline in its
natural forest cover (Bello, 1995). The impact of this
is wide-ranging. It has immediate impact on local
inhabitants who rely on the forest for subsistence
farming, but it has also had impacts on Thailand’s bio-
diversity and the ability of the ecology to withstand
other stresses. Policies may cover limits on de-
forestation and the implementation of re-forestation
programs.
Thailand also has pollution emission and control
policies in place but these are not vigorously enforced
(Poungsomlee and Ross, 1992). Pollution control and
abatement programs are required for water, air, noise,
and industrial pollution.
Stricter controls over the harvesting of renewable
resources is required to ensure that such resources are
not destroyed or forced below sustainable levels
(Duraiappah et al., 1999). Such resources may include
marine or land animals and vegetation. Ensuring
sustainability of these resources is a large part of
ensuring sustainability of welfare.
Increased attention on the provision of government
services and the actual mechanisms of government is
also required. Policies ensuring the protection of
political and civil freedoms and reduction of corrup-
tion and responsible management of debt can all
improve welfare. Both debt and corruption negatively
impact welfare within the Thai ISEW.
Even during periods of democratic freedom, the
welfare of Thailand has been negatively affected by
political corruption at all levels of society (Phongpai-
chit and Piriyarangsan, 1994; Linter, 1998). Corrup-
tion leads to inefficient allocation of resources
(Parnwell, 1996). This is perhaps the most difficult
policy change as its implementation must be prepared
and enforced by those with the most to lose. External
organisations, such as Transparency International,
may be required to assist in monitoring the effective-
ness of anti-corruption.
Whilst Thailand’s public debt does not compare to
the debt burdens of other developing countries, it is
still a matter of concern. In the past, public debt was
acquired for unproductive use such as fuel subsidies
(Dixon, 1999). Whilst short-term benefits may be
received in the form of cheaper or increased con-
sumption, the longer-term costs are greater. Servicing
debt results in fewer funds available for essential
services that can positively affect welfare such as
health and education spending. Various policies
capping debt or limiting it to productive uses only
could be considered.
Welfare can be enhanced with appropriate policies
focussing on issues of commuting and urbanisation.
Commuting has been recognised as a significant cost
of economic growth in Bangkok (Poungsomlee and
Ross, 1992). Within Thailand, this cost is extremely
high as Bangkok is one of the most primate cities in
the world (Dixon, 1999). Thai authorities have long
struggled with how to ease congestion in Bangkok but
with an additional 800 cars a day being registered in
Bangkok (Bello, 1995), solutions appear impossible.
Whilst the construction of new road lanes and the
Skytrain, have reduced some travel times, this area
must remain a priority for policy makers as it does
impact on welfare levels (Ross and Thadaniti, 1995).
The benefits of urbanisation have recently been
highlighted (Venables, 2003; Fujita et al., 1999),
however in extreme levels of urban density, such as
Bangkok, the social costs may be greater than the
economic benefits. Ten percent of the Thai population
lives in Bangkok making it one of the most primate
cities in the world. Policy measures might involve
decentralisation incentives for government depart-
ments, business and industry, disincentives for locat-
ing new or expanding existing industries within urban
centres, increasing services and rewards for those
living in rural areas, or actively encouraging reloca-
tion to rural areas.
Finally, a healthy spiritual sub-system results in the
protection of the most vulnerable within society from
being de-humanised (see welfare costs within the Thai
ISEW of commercial sex work). This may involve the
protection from exploitation of women, and children
from commercial sex work or from utter object poverty.
M. Clarke, S.M.N. Islam / Ecological Economics 54 (2005) 81–93 91
6. Conclusion
The paper empirically applied a ISEW to Thai-
land over a 25-year period, 1975–1999. The results
show that Thailand has begun to experience dimin-
ishing and negative welfare returns from economic
growth (termed stunting economic growth). These
results are not unique but have only been previously
found for developed countries (bar one exception).
As Thailand has begun to experience these diminish-
ing returns at such a low-income level should be of
great concern to policy makers who primarily rely on
achieving economic growth to improve welfare
levels. Further work is required in a number of
developing countries to determine whether the
experiences of Thailand are special or common and
following Lawn (2003) further work is required to
standardize ISEW composition and methodology to
make it more accepted by policy makers. If
diminishing and negative welfare returns from
economic growth can be reached prematurely then
alternative theories of development are urgently
required.
Acknowledgements
The authors would like to thank Dr. Adis Isranga-
kurn (Thai Development Research Institute, Thailand)
for his assistance in calculating the estimates for
environmental damage, Dr. Phil Lawn (Flinders
University) for his helpful comments, Professor
Wolfgang Schade and one other anonymous reviewer.
The authors also gratefully acknowledge the financial
support of the Australian Research Council (grant
LP0348013) in partnership with the Victoria Depart-
ment of Premier and Cabinet, Australia and World
Vision Australia.
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