Valuation of externalities for sustainable development
Andrea Ricci
Istituto di Studi per l’Integrazione dei Sistemi
Roma
Italy
Extended abstract
Relevance of externality valuation
Externalities are changes of welfare generated by a given activity without
being reflected in market prices. A cost (benefit) is considered external when
it is not paid (enjoyed) by those who have generated it. Externality valuation
provides major contributions to the formulation of sustainable development policies:
- on the one hand, supply side policies (infrastructure, products and services
in general) require that the relative merits of alternative options be assessed
and compared on an equitable basis. These policies can therefore directly benefit
from: i) the availability of an extended accounting framework for Cost Benefit
Analyses (CBA), where all social costs (i.e. both internal and external) are
considered in a consistent and homogeneous manner, and ii) the subsequent possibility
of comparing alternative investment options (e.g. through the assessment of
differential values)
- on the other hand, externalities, if not internalised, introduce market
distortions that should be corrected through regulatory and other (e.g. pricing)
interventions. Demand side policies (regulation, pricing and taxation) should
therefore systematically avail themselves of an accurate estimation of the absolute
value of externalities in order to define the optimal terms and conditions of:
- mitigation/abatement measures, and
- measures for the internalisation of externalities.
Abundant research has been carried out in the area of externality valuation
over the past decades, notably through the EU funded ExternE series. It has
produced a significant body of knowledge both in methodological terms and for
what concerns factual evidence supporting the integration of external cost accounting
into policy decisions. However, several important aspects are yet uncovered,
or insufficiently known.
- Sector-wise, two main areas have been so far investigated in detail, i.e.,
energy conversion and transport. Additional research is needed to define comparable
externality accounting frameworks for agriculture, industry and the services
sector, and, more generally, for land-use and water-use policies. There are
several dimensions requiring in-depth investigation in this respect. The level
of applicability of the existing accounting frameworks to new and different
sectors must be assessed, whereby burdens, impacts, receptors, and the physical
mechanisms linking them may vary considerably from one sector to another;
additional knowledge must therefore be gained on the nature of burdens, the
associated impact chains (exposure-response functions), and the monetary valuation
of such impacts.
- Similarly, externality research has concentrated primarily on a limited
- though crucial - set of external costs, i.e. those associated to the emission
of air polluting substances, to accidents, to global warming and, concerning
transport, to congestion. Noise pollution has been extensively investigated,
but the current body of knowledge is still insufficient, while other externalities
are altogether largely under-documented, such as e.g. visual intrusion, community
severance, water and soil pollution, odours. Additional research, both theoretical
and empirical (e.g., through ad hoc case studies) is needed.
- Moreover, energy and transport externalities are primarily negative (external
costs). In dealing with agriculture, as well as with land and water use in
general, the issue of multi-functionality arises, whereby any given policy
entails both external costs and benefits, pointing at the need for an accounting
framework that must be capable of integrating and balancing them accordingly.
Well-established approaches such as, in particular, the IPA (Impact Pathway
Approach), developed within ExternE and subsequently widely adopted worldwide,
must be checked against their potential ability to account for external benefits,
and to do so within a coherent valuation framework.
- Finally, and most importantly, the methodological approaches developed
for externality valuation assume that the starting point of the analysis is
a given technology, or a set of alternative technological options. What is then
calculated is the monetary value of the full set of impacts generated by those
technologies. In the wider framework of land and water use planning, the focus
is on the formulation of integrated policies for the sustainable use of land/water,
rather than on the ranking of a pre-specified set of alternative technological
options. This calls for a shift in the overall approach to external cost valuation,
whereby the accounting framework must then allow policies (rather than individual
technologies) to be evaluated. To a large extent, policies can be defined as
the combination of individual decisions, each directly or indirectly linked
to a choice in the selection or/and in the use of technologies.
Policy formulation and target setting: an integrated approach
Pure CBA (Cost Benefit Analyses), such as those associated to the use of externalities’
accounting frameworks, are often criticised for not taking into due account
social and political priorities that do not lend themselves to immediate and
reliable quantification. Critics contend that the economic theory often fails
to capture the true value of social, environmental, and other resources, whereby
a given policy may be identified as maximising efficiency from the economic
viewpoint, while failing to ensure the attainment of higher-level objectives,
such as, for instance, the preservation of the ecosystem, the fight against
long-term deterioration of natural assets, global warming, etc.
Responding to such legitimate criticisms calls for a complementary approach,
whereby policies should be formulated with the primary objective of guaranteeing
the attainment of sustainability targets, which in turn are geared to the intrinsic
characteristics of the ecosystem, and of natural assets in general. This leads
to the introduction of the well-known notion of thresholds, which can identify
the maximum level of pressure (social, environmental) that a given system can
absorb without facing irreversible collapse (the point of no return). While
such an approach is conceptually recognised as interesting and policy-relevant,
much progress remains to be made in order to establish a consistent and robust
methodological body for the quantitative assessment of thresholds characterising
natural assets such as agricultural land, coastal zones, seawaters and marine
systems, and ecosystems in general.
In fact, the two research streams outlined above (i.e. externality accounting
and threshold assessment) are often seen as reflecting parallel, and
at times even conflicting approaches to policy formulation, while they should
in fact be considered as complementary, and their integration accordingly pursued:
- in the CBA, externality-based approach, policies and technologies are
ranked according to their economic performance: impacts are valued in monetary
terms, and the overall economic performance is expressed by the final balance
between total social costs and total social benefits.
- in the threshold approach, policies and technologies are ranked according
to their relative performance in ensuring the compliance with minimum requirements
(the threshold values).
Combining the two approaches amounts to devising a method whereby one of the
two approaches is selected, and the other is included as a constraint in the
ranking process.
For instance, alternative uses of land can be analysed in terms of their social
external costs, along the entire IPA chain, leading to the monetary valuation
of costs and benefits of a given land use option. In parallel, thresholds can
be calculated to assess the carrying capacity of land in terms of absorption
of specific negative impacts associated e.g. to the growing of specific crops,
or to recreational use, etc.
The final ranking can be established by combining the two approaches: either
by introducing the threshold constraint to refine the ranking established through
externality analysis, or vice-versa.
In fact, several methodological options can contribute towards the integration
of the two approaches, with particular reference to Input/Output Accounting
(IOA), Strategic Environmental Assessment (SEA) and Multicriteria analysis,
and combinations thereof. Concerning IOA, promising developments can be expected
from the extension of the traditional IO structure so as to include the analysis
of the interchanges between economic sectors and natural assets, thus allowing
the capture of impacts that are usually unaccounted for (externalities).