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Sustainable Development

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Sustainable Development





INDICATORS

SD: Indicators

The elaboration of a suitable system of indicators

for sustainable development is one of the major

challenges facing contemporary science. The very

interdisciplinary nature of the issue, which is

preconditioned by the intricate and highly

dynamic system of inter-relations and inter-

dependencies between the socioeconomic

system and the natural environment, renders the

solution to the problem of indicator elaboration

exceedingly difficult.

SD: Indicators

• The individual indicators or systems of indicators that

have been used thus far are the product of two

relatively autonomous approaches.

• The first approach is based on the notion that

sustainable development can be measured and

assessed by using several subsystems of indicators

reflecting sustainable development’s various aspects—

environmental, social, economic, institutional, and so

on. Such is the approach of the United Nations

Commission on Sustainable Development (UNCSD) and

of the much-respected International Institute for

Sustainable Development (IISD) in Canada.

SD: Indicators

• The second approach puts its stakes on some “magical”

indicator of a maximally-high degree of aggregation

designed to reflect the entire range of indicators, covering

the various aspects of sustainable development.

• It is natural to assume that the implementation of the

second approach is considerably more difficult from a

methodological point of view because it means

characterizing numerous and varied direct links and

feedbacks between indicators from various subsystems.

Often, comparing these indicators along the lines of a

certain common trait (monetary, physical, extent of change,

and so on) contains too many conditionalities or is virtually

impossible at this stage altogether.

SD: Indicators

• Are these two approaches mutually exclusive? Arriving at

an integral and highly aggregated indicator is impossible

without simulating an indicator system and corresponding

subsystems grouped according to their congruity with the

various characteristics of sustainable development. The

issue we are focusing on is

• (1) whether eliciting a sufficiently reliable integral indicator

that could encompass and reflect the entire specificity and

variety underlying sustainable development is possible in

principle and

• (2) whether the sum of relatively independent indicators,

grouped in individual subsystems, could serve as a basis for

the solving the methodological problem outlined above.

UN: SD Indicators

• In 1997, at the 19th Special Session of the UN General

Assembly, the UNCSD tabled a proposal for the elaboration

of a system of 134 indicators of sustainable development

grouped by the four relevant dimensions: social, economic,

environmental, and institutional. The UN General Assembly

endorsed the proposal and gave its approval for the system

of indicators to be tested in twenty UN member countries.

The experience from the tests and the results from the

comparative analysis indicated the need for further

improvement of the systematization and formulation of

some of the indicators. This brought about a decrease from

134 to 58 indicators with the purposes of avoiding double

measurements and simplifying comparisons as much as

possible.

UN Indicators: ECONOMIC

• A. Economic Structure: GDP per capita, investment

share in GDP, balance of trade in goods and services,

debt-to-GNP ratio, total Official Development

Assistance (ODA) received or given as a percentage of

GDP

• B. Consumption and Production Patterns: intensity of

material use, annual energy consumption per capita,

share of renewable energy resource consumption,

intensity of energy use, industrial and municipal solid

waste generation, hazardous waste generation,

radioactive waste generation, waste recycling and

reuse, distance traveled per capita by mode of

transport

UN Indicators: Environmental

• A. Atmosphere: greenhouse gas emissions, ozone-depleting

substance consumption, ambient concentration of air pollutants in

urban areas

• B. Land: arable and permanent crop land area, fertilizer use,

agricultural pesticide use, forest area as a percent of land area,

wood harvesting intensity, land affected by desertification, area of

urban formal and informal settlements

• C. Oceans, Seas, and Coasts: algae concentration in coastal waters,

percentage of total population living in coastal areas, annual catch

by major species

• D. Fresh Water: annual ground and surface water withdrawal as a

percentage of total available water, BOD in water bodies,

concentration of fecal coliform in freshwater

UN Indicators: Social

• A. Equity: percentage of population living below poverty line, Gini Index of

Income Inequality, unemployment rate, ratio of average female wage to

average male wage

• B. Health: nutritional status of children, mortality rate of children less

than five years old, life expectancy at birth, percentage of population with

adequate sewage disposal facilities, population with access to safe

drinking water, percent of population with access to primary healthcare

facilities, immunization against infectious childhood diseases,

contraceptive prevalence rate

• C. Education: percentage of children reaching grade five of primary

education, adult secondary education achievement level, adult literacy

rate

• D. Housing: floor area per person

• E. Security: number of recorded crimes per 100,000 population

• F. Population: population growth rate, population of urban formal and

informal settlements

UN Indicators: Institutional

• A. Institutional Framework: national

sustainable development strategy, ratified

global agreement implementation

• B. Institutional Capacity: number of Internet

subscribers per 1000 inhabitants, main

telephone lines per 1000 inhabitants, research

and development expenditure as a percentage

of GDP, economic and human loss from

natural

UN Indicators: downsides

Naturally, countries with larger volumes of industrial

output, and that export their products to the

international market and thus meet certain demand,

will record higher levels of greenhouse gas emissions

if all other conditions of the compared countries

remain equal. In the first years of the transition to a

market economy, the Eastern European countries—

Russia included—marked a considerable decline in

their GDP and most notably in their industrial

output. This had a “positive” impact on the

environment because the manufacturing facilities

that used to pollute the environment had been

closed down or only partially used. An important

question to ask, however, is, Are lower greenhouse

gas emission indicators under such circumstances a

suitable sign for sustainable development?

UN Indicators: downsides





• The “debt-to-GNP ratio” and “trade balance” indicators on their

own, are also incapable of giving any ideas about sustainability or

lack of sustainability. Countries with equal debt-to-GDP (or GNP)

ratios are in different economic situations depending on the

capacity and viability of their economies.

UN Indicators: downsides

• The “energy consumption” indicator

(encompassing renewable and non-renewable

energy consumption) is far too general, as well. In

its essence, this indicator expresses an absolute

value that is not related to the efficiency of the

economy. In principle, it is possible to see a

scenario whereby the declining energy

consumption per capita of the population is a

sign of lacking sustainability and a shrinking living

standard, should this result from rising energy

prices rather than from growing energy efficiency.

Human Development Index

HDI (UNDP)

• This index is based on three relatively

independent components: (1) level of education,

(2) per capita GDP, and (3) life expectancy.

• Each of the components has a sub-index of its

own with an equal weight in the formation of the

composite index. In other words, the sub-indices

are equitable.

• In my opinion, both quantitatively and

qualitatively, the GDP per capita index directly or

indirectly reflects the other two indices or is

rather strongly influenced by them.

HDI Report 2010

http://hdr.undp.org/en/statistics/

• Very High DI: Norway, Australia, New Zealand, United

States, Ireland, Liechtenstein , Netherlands, Canada,

Sweden, Germany, Japan, Korea (Republic of),

Switzerland, France, Israel

• High HDI: Bahamas, Lithuania, Chile, Argentina ,Kuwait

Bulgaria No.58, Montenegro 49, Romania 50, Lybia 53

• Medium HDI: Fiji, Turkmenistan, Dominican Republic ,

China, El Salvador

• Low HDI: Burkina Faso, Liberia, Chad, Guinea-Bissau,

Mozambique , Burundi, Niger, Congo (Democratic

Republic of the), Zimbabwe

• Bulgaria No.

Index of Sustainable Economic Welfare

ISEW

Developed by Serafy et al. (1989); Daly (1989) has expanded

an index of a sufficiently high degree of aggregation:

ISEW = Cadj + P + G + W – D – E – N



where Cadj is consumer spending adjusted for income

inequality, P is non-defensive public expenditures, G is

capital growth and net change in international position, W

is non-monetarized contributions to welfare, D is the

defensive private expenditures, E is the cost of

environmental degradation, and N is the value of

depreciation of the environmental capital base.

• ISEW is a useful step forward in the effort to find

appropriate ways of aggregating indices from various

subsystems by bringing them down to comparable

monetary values.

The RioJo Dashboard System

• In 2001 the Consultative Group on Sustainable

Development Indicators (CGSDI), with the International

Institute for Sustainable Development (IISD),

elaborated and presented before the UNCSD the

Dashboard (Appendix 1), which is a system of indices

covering all aspects of sustainable development that

have been aggregated in a Sustainable Development

Index (SDI). The elaboration and adoption of this

approach by the UNCSD took place in connection with

the preparation of the World Summit for Sustainable

Development (WSSD) held in Johannesburg in 2002

and the presentation of a report on the comparative

analysis for the period 1990–2000.

The RioJo Dashboard System

• The assessments and conclusions in the report have been made in

compliance with the Millennium Development Goals (MDG).2

Countries and regions implemented this Dashboard system of

indicators to show the diverse nature of sustainable development,

on the one hand, and to assess the policies pursued by individual

countries or regional communities, on the other. This highly

aggregated indicator of sustainable development is made of three

relatively independent subindicator clusters, which reflect the

situations of three spheres, which include

• Environment—quality of water, air, and soil and levels of toxic

waste;

• Economy—employment, investments, productivity, income

distribution, competitiveness, inflation, and efficiency of material

and energy use;

• Society—crime rate, health, poverty, education, governance,

military spending, and international cooperation.

The RioJo Dashboard System

• As the suggested system of linked clusters indicates,

each cluster is represented by an index, aggregating the

indicators included in the respective sphere

(environmental, economic, and social). The three cluster

indices are aggregated again into an overall Sustainable

Development Index (SDI). The indicators themselves are

also represented in an index form. The environment-

related index, then, is based on the Environmental

Pressure Index (EPI) and the Ecological Footprint Index

(EFI),3 and the economy-related index is based on the

GDP and the Index of Economic Performance (IEP). The

Consultative Group on Sustainable Development at the

IISD thinks that the highly aggregated index they

suggested should be able to reflect the stock, flow, and

related interactions and management decisions.

The RioJo Dashboard System



In essence, the third cluster concerning the social sphere is under-

developed, although some possible indicators such as “happiness”

and “fulfilment of the human potential,” have been put forward.



The question about how so many subjective assessments will be

measured and will fit into the overall index has remained

unanswered.

Ecological Footprint of GDP

• The GDP carries abundant useful information about its

ecological footprint if the output value is compared with the

physical dimension (total and per unit) of the used input. The

concept of ecological footprint was first introduced by Drs. M.

Wackernagel and W. Reese in 1996. The energy and raw

material consumption for production of a unit of GDP is one of

the leading indicators for GDP’s spin-off effect, measured as an

ecological footprint. Given that all other conditions are equal,

the countries registering the lowest level of consumption per

unit of GDP are among those with the highest industrial

development and have the highest standard of living and high

HDI.

• The Eastern European countries, for instance, register from five

to eight times more electricity consumption per end-product

unit than do the developed countries. Factor analysis shows

that this is because of two main factors: lower technological

level and under-developed market incentives.

Ecological Footprint

• In my opinion, the input-output model of W. Leontief (1936, 1966),

Nobel Laureate in Economics, and its concrete orientation to the

impact of the material and energy flow on the environment are

mandatory instruments in the measurement of sustainability.

Nowadays, this approach to measuring physical flows by intensity,

direction, and effect on the economic process and the environment

finds an increasingly wide application because it operates with

specific, objective, and verifiable data, which gives reliable

information about the ecological footprint of GDP production. The

German scientist Schmidt-Bleek (1998) has suggested a

differentiated approach that measures both the quantity and type of

material resources that go into the production of a product unit (or a

service unit) and the waste emissions from the production of a

product unit (or a service unit). Two interrelated measures have been

proposed by Schmidt-Bleek: the Material Input per Service unit

indices (MIPS) and the “Ecological Rucksack” unit.

Ecological Footprint



• As an alternative approach, Bailey et al. (2000) divide the

domestic supply of raw materials into scrap and newly

extracted resources. This is an important differentiation as far

as the use of nonrenewable resources is concerned. This

model measures the ecological footprint through an input-

output model which shows the material flows in industrial

systems. This method has enormous potential in studying the

relationship between economic activity and the environment.

The authors of these methods have succeeded in including

other factors such as the international division of labor and

the share of natural resources used as factors of production—

which are either imported or obtained by the domestic

extracting industry—in their analyses.

A GDP Matrix: An Attempt for Systematic Approach

Gechev, R. (2005) Sustainable Development: Economic Aspects. University of Indianapolis

Press, pp.52-55







• The proposed matrix contains indicators that are connected

with the GDP in a direct, indirect, or relative way. As indicated

earlier, the indicators are expressed in an absolute or

dynamic form (in percentage terms) and as GDP derivative

indicators, which reflect the interaction between the

economic sphere and the other three dimensions of

sustainable development. The comparative analysis of the

stated indicators for an individual country, for a group of

countries, and especially at an international level would make

it possible to assess with a sufficient degree of accuracy the

state and trends of development in compliance with the goals

and criteria of sustainable development.

A GDP Matrix: An Attempt for Systematic Approach

Gechev, R. (2005) Sustainable Development: Economic Aspects. University of Indianapolis

Press, pp.52-55





• In my opinion, the most useful tool for assessing the

ecological footprint of GDP production would

indicate the energy and material intensity per unit of

the GDP disaggregated by sectors, industrial

branches, and types of production. Undoubtedly, the

countries registering the lowest material and energy

costs per unit of output are those enjoying the

highest living standards. They also possess the

biggest real and potential possibilities for

maintaining, restoring, or maintaining and restoring

the environment.

GDP: Is it a reliable indicator for sustainable

development?

• The claim that the GDP is a poor and even misleading indicator

of sustainable development is frequently encountered in the

specialized literature devoted to problems of sustainable

development. This argument does not seem to consider the

fact that the GDP indicator has not been created to measure

sustainability. It is highly illogical to define the GDP as a

“devilish” or “misleading” indicator, although such

qualifications can still be heard or read. There is little surprise

in the fact that we cannot measure atmospheric pressure with

a thermometer. The indicator in question works perfectly well

for the job it was created to do. To a large extent, the model

for calculating the GDP has been made universal; in other

words, it is one of the most reliable indicators for the purpose

of performing international comparisons.

GDP: Is it a reliable indicator for sustainable

development?

• Besides, an available, accessible, and reliable database for

each country and region exists, and GDP data compiled

therein encompasses a sufficiently long period of time for

trend analyses. Having been disaggregated in an

appropriate and targeted way, the GDP and its relative

derivatives can serve as a basis for performing a precise

assessment of sustainable development. The advantage of

this indicator is that it directly or indirectly reflects the

environmental, social, and institutional aspects of

sustainable development. The problem, then, is not

whether, but rather how, the system of disaggregated

indicators should be employed. My firm belief is that the

GDP is not a misleading indicator but has frequently been

misused.

GDP: Is it a reliable indicator for

sustainable development?

• If direct and indirect links exist between the

environment and the processes of manufacturing and

consumption, trying to find the complex of physical and

monetary GDP characteristics related to them is more

than logical. Neither the links nor the physical and

monetary GDP characteristics indicate the exact state of

the natural environment but give an adequate idea

about the nature of the processes of interaction taking

place, including the interactions from the sustainable

development point of view.

GDP: Is it a reliable indicator for

sustainable development?

• Which arguments support this thesis? All experts agree that

without economic growth, no social and economic

development is possible. The development of technologies,

social relations, the quality of life, and so on, is connected

precisely with economic growth. One of the preconditions for

the rise in the standard of living is the increase in the

production of capital and consumer goods and services. In

fact, the expanded production of capital goods and services is

indispensable for the increased output of consumer goods

and services. For people to consume more, more should be

manufactured—what should be maintained is the growth of

production. Because of this dependency, the level to which

the social sphere is developed, as an important aspect of

sustainable development, has a close positive relationship

with economic growth.



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