Sabatier's framework applied: A comprehensive LCA policy implementation
LCAs
are a tool for assessing the environmental impact of products. Think up four
ways in which governments can increase the use of LCAs through external control
and setting boundary conditions. Use Sabatier’s framework to assess the
potential effectiveness of external control vis-a-vis other options.
Life cycle assessment
(LCA) is an environmental assessment tool, which takes all the environmental
burdens connected to a product or service into account: from raw material
extraction to end-of-life (Klöpffer, 1997). It is the primary tool associated
to life cycle thinking (Heiskanen, 2002). When considering products, we now often
look beyond the production stage and rather take the entire physical life cycle
of a product into account (Heiskanen, 2002). Taking this approach ultimately
expands the scope of responsibility of actors, and ensures that environmental
burdens cannot be shifted away (Bauer et al, 2007). Burden shifting occurs when
alternatives cause adverse effects on the environment at other stages of the
life cycle (Bauer et al, 2007).
In this blog
assignment, we will therefore examine possible options for government to stimulate
the use of LCAs and finally assess them by using Sabatier’s framework. The two
ways of governmental influence, which we will examine are: shaping of boundary
conditions and external control.
Boundary conditions:
Setting boundary conditions attempts to change the mindset of the people. They
are incentives that are supposed to stimulate self-organization.
1) Best Practice: When setting boundary
conditions, I believe that governments should first of all implement it
themselves. By using LCA as a decision-making tool in governance, governments
can increase the use of LCAs by the private sector in several ways. Through
increased governmental use, for example, further methodological improvements
can be done. Also, a wide-scale governmental implementation could also offer
free public access to an “LCA database”, which helps standardize information.
By using LCAs, governments can therefore offer more validity to this tool and
make its use more practical.
2) Altering
market conditions: Following a wide-scale implementation of LCA,
governments can also set boundary conditions, by altering the market
conditions. Companies that publish LCA-related information about their goods or
services could be rewarded (e.g. subsidy).That way, governments could stimulate
firms to use LCAs.
External
control: As a means of policy implementation, external control occurs in form
of controlling the elements of a social system. In doing so, governments need
to set the scope of control, set the rules, and monitor the implementation.
1) Classification
system:
One possibility of exerting external control is by implementing a mandatory
classification system (e.g.: grades 1-10), for goods and services, based on LCA
results. This would work in a similar fashion to energy classes and could improve
the availability of information for consumers.
2) Market entry
boundaries: In order to complement boundary conditions, governments
could, for example, set a lower boundary for the classification system. That
way, only products and services with grades 4 and higher would be able to bring
their products to the market.
Sabatier’s Framework:
In
order to assess whether measures of external control in regards to LCA would be
effective, we will apply Sabatier’s framework. For the following analysis, the
statute we would examine is the large-scale implementation of LCA in order to
measure the environmental impact of goods and services.
Tractability of the
Problem:
The
first set of separate variables, which affect the effectiveness of governmental
institutions to achieve statutory objectives are aggregated into a summary
index of tractability. In essence, success depends on the difficulties of
measuring changes in seriousness of the problem, relating these changes back to
behavioral modifications, the diversity of the target group behavior, the
relation of target group size and population, and the extent of the behavioral
change required.
i)
Availability
of valid technical theory and technology: Availability of LCA
technology is not a problem. This tool has been around for many decades now and
it is theoretically clear, how it is to be used. The problem of LCAs is that it
is very assumption-laden and very case-sensitive. In LCAs, researchers often
face multi-functionality and allocation issues, which are solved on the grounds
of personal assumptions. Since these assumptions might vary on a case-to-case
basis, generalizations about best practice in LCAs are very difficult to make.
This sensitivity of LCAs ultimately leads to questionable overall validity.
ii)
Diversity of
target group behavior: The target group of such an LCA policy would
include all goods and services producing companies in a country. It would span
all types of industries. Furthermore, it would affect upstream / downstream
supply chain activities that are potentially located internationally. Even
though pressure opportunities may arise individually (Nokia case), it is
questionable how much influence economic actors really have on other supply
chain actors. The behavior and attitude of the target group is therefore highly
diverse.
iii)
Target group
as a percentage of the population: The target group (all producing firms)
basically comprises a majority of the entire national economy of a country. Due
the target group’s size and low isolatability, it is questionable whether broad
political support in favor of the program can be mobilized.
iv)
Extent of
behavioral change required: The behavioral change that is required is quite
large. Not only would companies have to invest in having LCAs done on their
supply chains, improving the identified “hot spots” will incur a lot of costs
as well. Due to the great amount of required behavioral change, successful
implementation may become problematic.
Ability to structure
implementation:
Another
set of variables, which affects the effectiveness of policy implementation, is
the objective’s capacity to structure the entire implementation process. This
is achieved, for example, if clear and consistent objectives are passed, if
significant financial resources back it and clear decision-rules are
implemented.
For
the implementation of this LCA policy, the case sensitivity of LCA remains
problematic. Since the assumptions and allocations vary by case, it will be
difficult to formulate clear and consistent objectives. Furthermore, it will be
problematic for firms to discern whether assumptions and allocations are
“correct” and where they could be potentially sanctioned for wrong LCA
implementation.
Lastly, I wonder about the necessary financial resources that would be necessary. While the amounts needed for an LCA might be calculated easily, there will be many unknowns related to the monitoring of LCA results and especially in regards to the implementation of changes. The government would possibly need to form a new controlling body and “consult” companies in the proper implementation. I fear that the financial resources that would be needed would quickly exceed initial calculations.
Non-statutory variables
affecting implementation:
The
last variables that influence the effectiveness to implement policies are
non-statutory variables. In essence, a well-drafted policy should be able to
withstand variations in political support and changes in public opinion. There
can be, for example, exogenous variables such as changes in socio-economic
conditions and attitudes of sovereigns and voter groups, which can have an
effect. In essence, this element probes how well a statute can survive in the
political landscape.
For
the LCA policy, potential problems may arise when socio-economic conditions
worsen, due to a recession, for example. Sovereigns and constituency groups
might be inclined to criticize the LCA initiative, due to its large costs and
its tendency to potentially “tell firms how to run their business”. When the
socio-economic situation worsens, constituents might be concerned about job
security and economic growth than about the environmental impact of goods and
services. In essence, environmental interests might still be a “luxury”.
The public support and the media attention might be especially problematic if the LCA initiative is undertaken only by one country. Popular belief is still that environmental concerns come at a trade-off to economic performance. If a country undertakes the endeavor by itself, the public and the media might be concerned about a worsened relative competitiveness.
Conclusion:
When
considering an LCA policy, one needs to take the complexity of LCA policy
implementation in regards to the globalized character of the world economy, the
significant costs related to implementation and the inherent lack of clarity
around LCA implementation into account. I believe that an LCA policy should be
a mix of boundary conditions and external control.
In
the short-term, governments should use boundary conditions and experiment with
the use of LCA in order to find best practice methods and isolate manners in
which this tool can be properly implemented. In my opinion, this would clarify
initial concerns about LCA, help quantify costs of implementation and ease
firms into the adoption process. Alongside government implementation, subsidies
could be given to firms for LCA use, in the hope that they would see the use as
a source for future competitive advantage.
Once
this is achieved, I envision an external control policy (option 1), which
offers concrete LCA information to consumers. Ideally, this would occur in form
of a classification system, such as the energy class system.
I believe, however, that the most important aspect concerns international coordination. Implementing an LCA factor or indicator needs to be done on an international level (by EU for example) in order to create comparability and solve potential supply chain complexities.
I believe, however, that the most important aspect concerns international coordination. Implementing an LCA factor or indicator needs to be done on an international level (by EU for example) in order to create comparability and solve potential supply chain complexities.
Sources:
Bauer, C., Buchgeister,
J., Hischier, R., Poganietz, W. R., Schebek, L., & Warsen, J. (2008).
Towards a framework for life cycle thinking in the assessment of
nanotechnology. Journal of Cleaner Production, 16(8), 910-926.
Heiskanen, E. (2002).
The institutional logic of life cycle thinking. Journal of Cleaner
Production, 10(5), 427-437.
Klöpffer,
W. (1997). Life cycle assessment. Environmental Science and Pollution
Research, 4(4), 223-228.
Sabatier,
P. A. (1988). An advocacy coalition framework of policy change and the role of
policy-oriented learning therein. Policy sciences, 21(2-3),
129-168.