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Newsletter and Technical Publications
<The Councillor as Guardian of the Environment>
An Essay and Workshop for Local Elected Leaders on Environmental
Governance
with Emphasis on Adopting Environmentally Sound Technologies (ESTs)
- Training for Elected Leadership -
Part I - Essay on the Councillor as Guardian of the
Environment
- ESSAY -
Man did not weave the web of life, he is merely a strand in it. Whatever
he does
to the web he does to himself. Chief Seattle, Native American Leader, 1857.
Definition and Summary
D. Tactics, Strategies and Approaches for Sustainable
Development
3. ASSESSING RISKS
Assessing Risks is the process of taking your awareness
and pursuing it further through additional data gathering, information
expansion, analysis and confirmation. Assessing risks is concerned with problem
finding, a diagnostic process that sheds light on barriers to sustainable
development and environmental protection. Assessment results in greater clarity
regarding the situation you hope to influence in your policies, decisions and
actions as elected leaders in your community. Assessment should increase your
confidence in these policies, decisions and actions; confidence that they will
produce the outcomes you want.
In the literature you will find a number of assessment
techniques with, sometimes, rather confusing names. Out of this host of
assessment methods, we want to briefly introduce only two: Environmental Risk
Assessment (EnRA) and Environmental Technology Assessment (EnTA). These are
major strategic planning tools for decision making in environemental management.
While EnRA evaluates the environmental status of, e.g., a city, to predict
future consequences of exposure to hazards, EnTA mainly focuses on the
ecological opportunities and risks of new technologies. Environmental Technology
Assessment, however, would also include in the analysis - to give an example -
trade-offs between economic and ecological impacts.
EnTA can be done in the context of problem finding
(acknowledging that the technology itself can be problematic) and as a process
for evaluating alternative technical solutions to a problem. In the first
context, EnTA is integral to the risk assessment. In the second, it becomes a
legitimate tool for evaluating options for action. The case studies that follow
are designed to illustrate the range of possibilities in the environmental risk
assessment process. But before we present them, here are some concerns about
relying too heavily upon experts to conduct either of these assessment tasks.
| Assessment Traps to Avoid |
Assessments, either of the risk or technology kind, can become so complicated
that they are taken over, or perhaps handed over, to the experts. That may have
been part of the problem in Nakuru where the flamingos departed the local scene
and took most of the tourists with them. Technical specialists are essential to
understanding and resolving most environmental challenges and should be brought
into decision making and problem solving processes. However, we are concerned
that local government councils often allow the assessment process to be taken
over by experts and specialists, or they hand it over to the
technical specialists without providing for proper oversight.
(Overseer: this is another of those important roles
you have as an elected leader.
Fortunately, it is covered in one of the companion handbooks in this series.)
Another potential trap in using the assessment tool is to become over
confident in the conclusions that can be drawn from the data, when you and your
elected colleagues make decisions. There is nothing as reassuring as a bunch of
complicated data, even when it is wrong. Think about it. How many times have
you, as a councillor, been lured into a decision based on the "validity of
the numbers"? While we have waved this red flag of warning about
over-reliance on the "predictability" of hard data, we also recognize
the importance of technical experts and their counsel on
environmental/development issues of increasing complexity.
And, of course, there is the trap of believing a comprehensive assessment of
some environmental risk in your community, at some specific point in time,
removes the need to continue the assessing process over time. The dynamics of
interplay between physical, economic and social development, and the natural
environment, is such that assessment must be an ongoing process.
| Examples of Risk Assessment and Appropriate Technology
for Assessment |
Assessment doesn't have to be complicated or comprehensive, although it can
be both. In the three cases that follow, we discuss three very different
approaches to environmental risk assessment.
- The comprehensive environmental risk assessment carried out in Lancashire
County, UK had many objectives, including: establishing baseline information
on a wide range of environmental risks; identifying information gaps; and,
enlisting the involvement and support of 65 key institutions, representing
all major stakeholders, in the information gathering and analysis process
with an explicit assumption that they would participate in problem solving.
- The environmental risk assessment conducted on the Paco Estuary (in
metropolitan Manila) had a much narrower mandate and objective. It was
conducted by an non-governmental organization and paid for by a private firm
operating within the community. The corporation's motive in having the
assessment conducted was largely self serving (to clear its name by
determining the real sources of pollution along and in the Paco Estuary) but
it resulted in positive action taken by the community to address the sources
of pollution
- In West Africa, an agricultural research institute undertook an
anticipatory, or prevention oriented, environmental risk assessment project
that turned the sequential process of assessing risks and problem solving
(which also requires environmental technology assessment) on its head. They
initially focused on the introduction of appropriate technologies that would
address a range of practical concerns including sustainable development and
preservation of the environment.
At the Second Annual World Bank Conference on Environmentally Sustainable
Development, 1994, Elisea Gozun, Coordinator, Metropolitan Environmental
Improvement Project, Manila, reported on the role of community governance in
urban environmental management. While her presentation covered a wide range of
topics and experiences in the metropolitan area, we want to focus on her
comments about how one community came to grips with a pervasive pollution
problem through an assessment conducted from the outside.
While there was general awareness of the pollution problem in the
community, a large multinational corporation was consistently thought to be the
major contributor to the pollution in and along the Paco Estuary. Perhaps out of
self defense, the corporation commissioned an NGO to study the problem, in other
words, to carry out an assessment. When the assessment was completed, it
revealed the Paco Public Market as the primary culprit. Assessment information
isn't worth much if it isn't shared and acted upon, so a public workshop was
held to share the results. Recognizing the need for partners and coalitions in
any permanent resolution of the pollution problem in and along the Paco Estuary,
the sponsors invited a wide range of stakeholders to attend. They
included vendors, hawkers, market administrators, local elected officials,
corporate officers working in the community, and representatives of metropolitan
and national government agencies.
While the main source of pollution had been identified though an external
assessment, it didn't stop the participants from pointing their fingers at
everyone else as the culprit. Ultimately, the blame placing stopped and the
major contributors of pollution signed an agreement to plan and implement a
waste minimization project to stop the pollution of Paco Creek.
Assessment alone won't overcome sources of environmental degradation. As Ms.
Gozun pointed out in her presentation: The community must understand the
problem and must be willing to act; and, individual members of the
community must have a sense of ownership in the solution. While many
organizations (public, NGO and private) contributed to the success of the Paco
Environmental Enhancement Project, the most heartening contribution came from
the street vendors and hawkers. They spent personal time and effort to clean the
Paco Estuary and hired their own street sweeper to help sustain the
environmental quality resulting from the restoration effort.
Lancashire County in the west-central part of the island of Britain lives
with an environmental legacy that dates from the beginning of the industrial
revolution. With a traditional economic base of mining and manufacturing based
on technology that largely ignored environmental consequences, the county has
had to work uphill to overcome past indiscretions against nature. But this awareness,
coupled with a vision of what their future can be, in terms of
sustainable development, is a story worth sharing. In 1990, the County Council
of Lancashire (an urban community of 1.4 million people), motivated by the
public's concern with both local and global environmental issues, funded the
initial step in a six stage strategy to improve the quality of the local
environment. This initial phase, financed solely from local tax revenue, was a
comprehensive environmental audit (assessment) designed to "provide
the people of Lancashire, and all interested parties, with the first
comprehensive picture of their environment."
The audit, compiled over two years by a full time staff of five, resulted in
a 325 page document that details all aspects of the county's environment, from
topography to types of wildlife habitat to sites of significant noise pollution.
Since most citizens can't be expected to read such a heavy tome, the county
condensed the report to 60 pages for dissemination to citizens and other
interested parties.
While the preparation of the audit was primarily the responsibility of the
five person team, they had lots of partners and coalitions to work
with. One important partner was the Geographic Information System staff
while an invaluable coalition was the Lancashire Environmental Forum, a
broad-based environmental stakeholders organization formed by the
Steering Committee of the County Council. The Forum represented over 65
organizations within the county, including government agencies, industry, other
forms of local government, NGOs, community groups, and academic institutions.
The breadth of representation was designed to accomplish several objectives:
- to assure the broadest possible understanding of environmental conditions
and attitudes within the community;
- to increase ownership of the audit and its consequences beyond the
boundaries of local government;
- to serve as a focus for implementing recommendations and actions resulting
from the audit; and
- to serve as conduits for information assembled by the audit team.
All are important, but we want to emphasize the last point. The data used in
the audit (assessment) was not created by the team but rather gathered from
other sources. The council recognized early on that most of what they needed to
know about the environment in their large urban community was already known by
some organization or person. The audit team's task was to ferret out the
information and bring it together into a cohesive document.
The Green Audit had six objectives, all designed to turn the information and
data in the audit into follow up actions. In other words, to assure it would not
become a dust collector in the county's archives. These were to:
- Provide a comprehensive statement and analysis of the present condition of
Lancashire's environment.
- Establish baseline information against which changes in the county's
environment could be measured in the future.
- Identity gaps in available information.
- Furnish data essential to the task of deciding which actions to take on
the environment.
- Help the county and other levels of government assure their services are
delivered in an environmentally friendly manner.
- To enlist support of the people and organizations of Lancashire and other
bodies in protecting the environment of the county.16
The Food Research Institute in Ghana saw the need to introduce appropriate
technologies to reduce post-harvest losses and to provide technical support for
the development and growth of the local food processing industry. Assessment
techniques included direct observation, individual and group interviews with key
stakeholders, including the target beneficiaries, and review of available
written information sources about the history of local post-harvest losses and
alternative technologies to reduce the losses.
Since the two main crops focused on by the Institute were fish and cassava,
the socio-economic issues were quite different. Working closely with the
fishermen and farmers, the Institute developed a list of constraints, needs and
priorities. Criteria that influenced the final design of new technologies
included:
- alleviation of drudgery;
- technical efficiency;
- ease of operation and maintenance
- choice of readily available, affordable and renewable energy sources;
- capacities to meet individual, group or community needs;
- flexibility of design to allow for adaptation; and
- affordability of technology by the target group.
The final criteria were important to assure that adoption of new technology
wouldn't suddenly shift production to another socio-economic group, either
within the community or beyond its boundaries. Affordability and sustainability
were enhanced by opportunities to manufacture equipment and spare parts locally.
The assessment phase included pilot projects where the new technology was
tested in relation to the criteria listed above. When Abigail Andah from the
Food Research Institute spoke about their efforts at a Regional Workshop on
Technology Need Assessment in Support of the Transfer of Environmentally Sound
Technologies, she reported that over 100 towns and villages in Ghana and
neighboring counties had adopted sustainable technologies to process and
preserve two of the main food products in the region.
We have looked at the use of assessment tools in three very different
contexts as they relate to environmental issues and your role as Guardian
of the Environment: assessing the viability and acceptance of new
environmentally sound technologies along the coast of West Africa; finding the
real source of pollution in one of the communities within the metropolitan
complex of greater Manila; and, finally, a look at how an old industrial city in
England built an information base for environmental decision making based on a
collection of assessments carried out by other organizations.
| More Specifics About Environmental Risk Assessment |
The techniques used in environmental risk assessment are not new. In their
rudimentary form they date back to the last century, evaluating the probability
of a particular adverse effect occurring to humans or the environment as a
consequence of specific actions. The actuarial tables estimating the life
expectancy of men and women for insurance purposes is an example of the early
use of the technology. The process of assessing environmental risk to humans
grew more sophisticated over the years as exposure to certain elements became
more prevalent. For example, the level of chemical risk to the human body was
equated by looking at two fundamental variables, toxicity and exposure.
According to the experts, a risk does not exist unless two criteria are met:
- The agent has the inherent ability to cause an adverse effect.
- The receptor (individual organism or population) of concern is in contact
with an agent for long enough, and at sufficient intensity, to elicit a
response.
One of the authors had a direct experience with this assessment process when
he was living in a village in south Asia many years ago. After becoming the host
of some nasty amoebae, he sought a physician who fed him arsenic, but only
enough to kill the squatter population (no pun intended). In this case the Human
Health Risk Assessment (HHRA) was measured between two adverse consequences.
EnRA becomes more complicated when it takes on the challenge of estimating
the environmental risk to ecological systems (expanding the definition to
encompass the risks to all non-human elements in the environment). The experts
call this technique Ecological Risk Assessment, or EcoRA. And, they point
out three distinct differences between HHRA and EcoRA.
- EcoRA can consider effects beyond those on individuals of a single species
and may examine population, community, or ecosystem impacts.
- There is no one set of assessment endpoints (environmental values to be
protected) that can be generally applied.
- Evaluation of the possible effects of non-chemical stressing agents are
integrated into the Ecological Risk Assessment.17
Let's see if we can make sense out of these differences from a
non-technician's perspective. Let us assume that some highly insensitive
entrepreneur has created a junk yard of spent vehicles in your residential
neighborhood. While it offends your aesthetic sensitivities, you are certain
that it also has an impact on the community and larger ecosystem. For example,
harbouring rats and eventually leaching certain unfriendly elements into the
nearby estuary. The environmental values to be protected (assessment endpoints)
are also a bit unclear; otherwise, why are there so many automotive junkyards in
the world. Finally, the ecological risk assessors factor in the non-chemical
stressing agents. You and your neighbors are suffering from emotional anxiety
and visual deprivation, not to mention the possibility of some new strain of
bubonic plague caused by rats ingesting high levels of used rubber and polyester
seat covers into their daily diet. Given these fundamental differences, we are
probably dealing with an ecological risk rather than a human health risk but an
environmental risk nevertheless.
While this interpretation of the basic differences between the two types of
environmental risks is no doubt simplistic and perhaps even misleading, it
emphasizes the dilemma most lay persons are confronted with when trying to make
sense out of complex, long range ecological impacts of every day living
arrangements we have come to take for granted. For most of us it is difficult,
if not impossible, to fathom the ecological impact we are having on the ozone
layer every time we push the release button on a pressurized can of whatever.
And yet, this individual act of indiscretion when multiplied by billions of
similar acts around the world on any given day, if not restrained, will surely
impact at some point on our ability to survive as residents of Planet Earth.
Human Health Risk + Ecological Risk = Economic Disaster in
Surat, India and Other World Communities
When the Black Plague swept across Europe and
Asia in the Middle Ages, it killed about one fourth of the population in
Western Europe. As environmental and health standards improved around the
world, the fear of plagues and recognition of the human devastation they
could bring receded from our collective memories. Consequently, the world
community was shocked when the Black Death scourge struck Surat, India in
1994. It was a chilling reminder of how rapid urbanization and the
deterioration of the urban environment can bring people into contact with
forgotten disease vectors.
While the outbreak of pneumonic plague in Surat was brought under control
quickly, (keeping the death toll under 60), the human health risk was
potentially devastating and the ecological risk factors still remain.
Urban crowding and poor sanitation can provide ideal conditions for the
spread of this type of plague. When the squalid living conditions that
exist among the urban poor in Surat were combined with two natural
disasters in the area (an earthquake and monsoon flooding), experts
believe the stage was set for an influx of plague infected rats into the
city from the surrounding forested areas.
This type of plague, if left untreated, can kill 100% of its victims and
the fear of an epidemic in Surat was so intense that one quarter of the
population of 2.2 million fled the city within four days. Fortunately, the
death toll was relatively minor but the economic toll on the city and
country was temporarily devastating. In financial terms, it was estimated
the plague cost the Indian economy over $600 million. More than 45,000
people canceled their travel plans to India, and the hotel occupancy
dropped as low as 20% in some cities. Many countries stopped air and sea
shipments to India altogether. In total, exports from the country suffered
a $420 million loss.
Surat is not an isolated example of the cost of ignoring the negative
potential of environmental consequences to the social and economic fabric
of urban communities. Vector borne diseases are largely preventable and
the cost of prevention is often a fraction of what it can cost to engage
in damage control once the "rat" is out of control.18
The challenge for local elected officials, as Guardians of the
Environment, is to make sense out of these differences so they can be
translated into environmental policies, programmes and actions that foster
sustainable development in their individual communities. In order to
undertake an ecological risk assessment, or more broadly defined, an
environmental risk assessment, the UNEP International Environmental
Technology Centre (IETC) recommends a three step process:
- Problem formulation;
- Analysis of the potential exposure and ecological effects; and,
- Risk characterization (integration of the iterative analysis of
exposure and effects).
Problem formulation, or what we prefer to call problem finding, is
taking your collective awareness of the environmental concerns you
believe are most critical (as expressed within the council and community)
and focusing in on them. To formulate the problem is to hold an intense
dialogue with it (e.g. Why are you a problem to us? Where are you a
problem? When? How? What would happen if we didn't take any action to
solve the problem? And always back to Why?). What you are looking for in
this problem finding phase are quantitative and qualitative descriptions
of the environmental conditions that provide widespread assurances that
this is a problem you, as a council and community, are willing to deal
with. Not all people will find (define) an ecological problem in the same
way. Values and personal interests will quickly interject themselves into
the dialogue and that's where the second two steps in the process can be
useful in moving the assessment along.
The analysis stage pinpoints the extent and short and long range
consequences of the environmental exposure confronting the community. The
final step in the EnRA is the integration of these two factors (exposure
and effect), a process the experts call risk characterization.
EnRA can be a complex and technically demanding process, one which will
require your council to call on the knowledge, skills and experience of
specialists. Often these experts are within your community. Other times
you may have to search beyond the "city limits" for technical
assistance. (Remember the earlier comment on the scarcity of ecologists in
some parts of the world?) Nevertheless, it is important to realize that
technical information is only part of the equation when it comes to
solving complex environmental problems. Common sense and grassroots
experience in dealing with the consequences of the problem (long before it
became acknowledged by the council as a "problem") are equally
important in any effort to seek long term and sustainable solutions.
We have talked about the importance of involving key stakeholders in the
process of managing sustainable development. At no stage in that process
is it more important to select the stakeholders with care and deliberation
than in the assessment of environmental and ecological risks.
As IETC reminds us, it is imperative that environmental risk assessment
be based on mutual learning, sharing, and defining fears, expectations,
hidden agendas, and values. Change, differing concepts of the world, and
,most importantly, the concept of human dignity must be recognized. After
all, risk management is, in the end, a human judgment endeavor. |
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