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Green Accounting

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Title: Green Accounting


1
Green Accounting
2
EU Policy Context
  • Lisbon (economic and social)
  • Gothenburg (environment)
  • Climate changeĀ 
  • Sustainable transportĀ 
  • Public health
  • Resource management
  • Green accounting links economic and environmental
    objectives

3
Overview of Presentation
  • Green (environmental) accounting
  • Rationale
  • Elements of Green Accounting Theoretical
    conceptual basis
  • Empirical progress in different contexts
  • Conclusions for research and practical
    applications.

4
Rationale for conventional accounting
  • Measurement of economic activity - production
    GDP
  • Often used as indicator of welfare
  • Two elements of accounts
  • Changes in Stocks of Capital - Investment
  • Measurement of production/output Flows -
    Consumption

5
Standard National Accounts (SNA) framework
  • NNP C I D X M
  • Where
  • NNP Net National Product
  • C Consumption
  • I Investment
  • D Depreciation
  • X Exports
  • M Imports
  • Misleadingly used as measure of welfare welfare
    not proportionate to consumption of produced goods

6
Green accounting rationale
  • The effect of mankinds activity upon the
    environment has been an important policy issue
    throughout the last part of the twentieth
    century.
  • increasing recognition that continuing economic
    growth and human welfare are dependent upon the
    services provided by the environment
  • Source The United Nations Handbook of National
    Accounting - Integrated Environmental and
    Economic Accounting
  • Economic Environmental linkages have
    implications for meso- and macro-economic
    management
  • Meso/macro-economic management more responsive to
    environment if environmental indicators exist

7
Elements of Green Accounting - Outline
  • Environmental services
  • Ecosystem life support systems
  • Landscape
  • Environmental damages
  • Pollution flows e.g air water quality
  • Defensive (environmental protection) expenditures
  • e.g. noise reducing windows IPPC technologies
  • Resource depletion
  • Non-renewables renewables

8
Empirical progress in Environmental Accounting in
different contexts some evidence
9
  • UN initiative on Green Accounting UNSEEA (1993,
    2000, 2003)
  • System of integrated Environmental and Economic
    Accounting (SEEA) complements SNA method for
    measuring economic activity
  • Adds environmental information to existing
    Input-Output economic data
  • Physical stock and flow tables
  • Hybrid (physical monetary) stock and flow
    tables
  • Methodological guidance on resource depletion,
    degradation, defensive expenditures

10
Physical monetary stock and flow tables
  • Often known as NAMEAs (National Accounting Matrix
    including Environmental Accounts).
  • Physical flow accounts include four types of
    flow
  • products (produced in the economic sphere and
    used within it),
  • natural resources (mineral, energy, biological),
  • ecosystem inputs (air and water) and
  • residuals (solid, effluent, emissions).
  • Each of these accounts is expressed in terms of
    supply to, and use by, the economy.
  • i.e. tables represent the flows between the
    economy and the environment.

11
An indicator of weak sustainability genuine
savings
  • Genuine Savings monetary savings less the
    depreciation on manmade capital less the
    depletion of natural capital. (From S Iv
    identity)
  • Value of changes in economys overall capital
    stocks.
  • Negative genuine saving corresponds to
    unsustainability, since if depleting capital
    stock, can receive lower welfare from it in
    future
  • Genuine Savings rates low or negative for
    Sub-Saharan Africa and for Middle East and North
    Africa.
  • Assumes all capital is substitutable

12
Genuine savings for Tunisia, as of GDP
13
The Index of Sustainable Economic Welfare (ISEW)
  • ISEW (Daly and Cobb (1989))
  • current welfare should be measured as the current
    flow of services from all sources, rather than
    current output of marketed goods
  • E.g.
  • value for leisure time to correct for the fact
    that welfare could increase while NNP decreases
    if people choose to work less
  • higher incomes of urban residents are
    compensation for externalities connected with
    urbanisation and congestion, ? proportion of
    income should not be included as welfare

14
  • The Index of Sustainable Economic Welfare (ISEW)
  • ISEW
  • Consumption Investment Extra-Market services
    Consumer Durables Services Services of Roads
    Public Health Education Consumer Durables
    Expenditure Private Defensive Expenditure on
    Health /Education Advertising Commuting
    costs Pollution costs cost of loss of
    ecosystems resource depletion costs Long
    term environmental damage
  • Applications at national level UK, Sweden,
    Netherlands, Italy, Poland, Austria
  • Applications at local level Siena (Pulselli et.
    al. 2006)
  • Problem mixes sustainability and
    welfare issues in single measure

15

Index of Consumption Corrected for Environmental
Damage (ICCED)- EC Greensense project
  • ICCED developed
  • to demonstrate how well-being changes over time
    if sustainability standards imposed and effects
    of environmental damage are accounted for.
  • corrects for environmental damage and expenditure
    incurred under sustainability policies
    (similarities with local EcoBudget initiatives
    e.g. Roma)

16
Sustainability targets analysed under the
GREENSENSE project
17
Greensense Environmental impacts on welfare (UK)
18
Greensense ICCED Measures - UK
19
Summary of Empirical initiatives
  • NAMEA includes environmental issues within
    standard accounting framework
  • Genuine savings sustainability-related decision
    rule
  • ISEW broader interpretation of welfare
  • ICCED includes welfare effects of meeting
    sustainability targets

20
Conclusions on Green Accounting
  • Recognition of need to address both current
    welfare and sustainability issues from
    macro-perspective
  • National and international initiatives (e.g. UN
    SEEA, 2003) are developing improved methodologies
  • Variety of initiatives reflects lack of consensus
    on priorities and methods
  • Local applications of methods can reflect
    regulatory responsibilities but may be difficult
    to define sustainability at this scale?
  • Applications very data-hungry and modelling
    intensive
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