Abstract
This paper reports on the development and application of a method
for establishing environmental priorities. The paper begins by reviewing
two common methods for identifying environmental priorities: state of
environment reporting (SER) and comparative risk analysis (CRA). The
review shows that SER does not provide clear priority ranking and CRA,
while providing clearer priority rankings than SER, is very costly to
undertake. An alternative method is developed based on an environmental
expert survey. This alternative technique, which is termed the expert
survey method (ESM), is applied to a case study region (British
Columbia, Canada) to illustrate its strengths and weaknesses. The
principal advantage of ESM is that it produces comparable results to the
more sophisticated CRA at a much lower cost and with greater
flexibility. Limitations of ESM are that the results are not necessarily
representative because they are based on sampling an elite segment of
society and they do not incorporate the benefits of inte ractive
learning. These limitations can be overcome by complementing ESM with
more inclusive approaches such as collaborative planning and using
subsequent steps in the process such as workshops to achieve interactive
learning. If these limitations are addressed, ESM can be a highly
effective tool for identifying environmental priorities. The paper also
provides a detailed summary of the ESM findings for the case study
region. These results from the case study provide a framework for the
development of an environmental agenda in a Canadian context.
Cet article porte sur la creation et l'application d'une
methode d'etablissement des priorites environnementales. Il examine
d'abord deux methodes habituelles: les rapports sur l'etat de
l'environnement (REE) et l'analyse comparative des risques
(ACR). Ce bref examen demontre que les REE ne fournissent pas une
hierarchisation claire des problematiques, tandis que I'ACR (qui
fournit une priorite de rang plus claire) est tres couteuse. Une
solution de rechange est proposee, creee partir d'un sondage
d'experts de l'environnement (SEE). Cette methode est
appliquee a une etude de cas regionale (la Colombie-Britannique, au
Canada), afin d'en illustrer les forces et faiblesses. Le principal
avantage du SEE est qu'il produit des resultats comparables a
I'ACR, a un bien moindre cout, et qu'il offre plus de
souplesse. En revanche, ses resultats ne sont pas necessairement
representatifs car ils sont bases sur un echantillonnage d'un
segment de l'elite de la societe et qu'ils n'integrent
aucun des benefices associes a l' apprentissage interactif. Ces
limites peuvent etre depassees en integrant aux SEE des approches plus
inclusives, comme la planification collaborative et l'apport
d'etapes subsequentes dans le processus (des ateliers, par
exemple), afin d'integrer l'apprentissage interactif. Si de
telles solutions sont apportees, les SEE pourraient etre des outils tres
efficaces dans l'identification des priorites environnementales.
Cet article presente aussi un resume detaille des resultats du SEE sur
les priorites environnementales dans l'etude de cas regionale, afin
de contribuer au developpement de la question environnementale dans un
contexte canadien.
Key Words
Environmental planning, environmental priorities, expert survey
methods, environmental risk assessment, state of environment reporting
Introduction
The purpose of this paper is to report on the development of a
method to identify environmental priorities and report findings from its
application to a case study in British Columbia. Development of the
method was in response to a request from the British Columbia government
to establish provincial environmental priorities at minimal cost within
a six-month period.
The paper begins by reviewing two of the most commonly used methods
for setting environmental priorities in North America: state of
environment reports (SER) and comparative risk analysis (CRA). The
review is followed by an outline of the Expert Survey Method (ESM), an
alternative based on a survey of environmental experts. ESM is designed
to identify environmental priorities, assess environmental policy and
generate an environmental mitigation plan. The method was applied to a
case study of expert respondents in the Province of British Columbia.
Results are reported here to illustrate strengths and weaknesses of this
method in comparison to CRA and SER and to identify environmental
management priorities in a Canadian context.
Priority Setting in Environmental Management
Priority setting is recognised as an essential step in the
environmental management process by a wide range of experts including
government agencies (Minard, 1996; USEPA, 1987, 1990), independent
research institutes (Carnegie, 1993; Davies, 1996; Finkel and Golding,
1994) and professional management associations (National Academy of
Public Administration, 1995). The reason for this is that empirical
research shows that setting clear priorities can increase the
effectiveness of environmental management by ensuring that resources are
allocated to the best use (Breyer, 1993) Public opinion research also
shows strong support for systematic environmental priority setting
(Graham and Hammitt, 1996).
One approach for identifying priorities is state of environment
reporting (SER). Recent Canadian examples include both international
reports (NACEC, 2002) and national reports (Canada, 1996). Some
provinces have instituted SER as part of ongoing management process
(e.g. BC-MELP, 1998, 2000). These reports provide a comprehensive
assessment of the state of environment by using a set of environmental
indicators such as air pollution levels and number of species at risk to
gauge the health of key environmental components. The assessment of
trends is intended to assist environmental managers in setting
priorities. However, the utility of SER for setting priorities is
limited because the absence of comparable indicators precludes explicit
ranking of problems.
A more explicit method for setting priorities is comparative risk
assessment (CRA). This technique was developed by the United States
Environmental Protection Agency (USEPA) in 1987 to establish
environmental management priorities for the United States government.
The technique has since been applied in more than 36 regions in the
United States (Minard, 1996).
The first step in CRA is to identify the environmental hazards to
be assessed. A review of evidence on the relationship between the hazard
and human health follows. Exposures are then estimated and health
impacts are forecast for each hazard. Finally risks are ranked according
to overall health impacts. In most studies, human health and ecological
rankings are provided in separate categories because human health risks,
measured by deaths, and ecological risks, measured by damage to the
system, are difficult to compare.
CRA has a number of deficiencies (Finkel and Golding, 1994;
Commoner, 1994; McCloskey, 1994; Hornstein, 1992; Davies, 1996). One
problem is that CRA is resource intensive (Anderson, 1996): costs are
high and completion time is extensive, involving on average three years
by large teams of experts. Second, CRA does not give clear results
despite its comprehensiveness because indicators used for human hazards
and ecological hazards are not comparable. Even where the same
indicators are used, such as human death rates, results are not clear
because of the high degree of uncertainty over impacts (National
Research Council, 1994).
A third, criticism is that CRA excludes many variables considered
important by the public (Krimsky and Golding, 1992) -- results of CRA
often differ widely from the public ranking of risk (Minard, 1996). This
has led some critics to conclude that CRA is inimical to democratic
principles because it substitutes scientific judgement for public values
under the guise of objective research (Hornstein, 1992). It is alleged
that in some instances this reliance on scientific proof can repress the
precautionary principle and defer mitigative measures until negative
impacts are verified (McCloskey, 1994). Given these problems, the public
and key decision-makers are often uncomfortable with CRA results.
Consequently, CRA findings have not had a significant impact on resource
allocation (Minard, 1996).
In sum, the two most commonly used techniques for selling
environmental priorities have serious deficiencies. SER does not provide
clear rankings. Although CRA provides clearer rankings than SER, they
are still ambiguous and the costs are high. These factors, as well as
the limited impact on policy have led some critics to question the
utility of CRA. At the same time, critics acknowledge the importance of
utilising scientific judgements in the priority setting process. The
challenge is to find a method to set priorities that utilises scientific
knowledge and is easier and less costly to apply. The purpose of this
paper is to report on the development and application of an alternative
method that meets these objectives.
Environmental Survey Method (ESM)
An alternative to a costly CRA or SER is to undertake an expert
based survey to help establish environmental priorities. A small
advisory group of environmental experts was formed to assist the
research team in the design of the method, which is outlined in Figure
1. The method and results are outlined in detail in Gunton and Ponsford
(2000).
The first step in ESM is for the research team to complete a review
of relevant literature regarding environmental issues, the state of
knowledge on these issues, and to identify key environmental
researchers.
COPYRIGHT 2002 Wilfrid Laurier
University Reproduced with permission of the copyright holder. Further reproduction or distribution is prohibited without permission.
Copyright 2002, Gale Group. All rights
reserved. Gale Group is a Thomson Corporation Company.
NOTE: All illustrations and photos have been removed from this article.