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FORUM
Environmental Impact Assessment Under the Mackenzie ValleyResource Management Act: Deliberative Democracy in Canada’sNorth?
Patricia Fitzpatrick Æ A. John Sinclair ÆBruce Mitchell
Received: 27 August 2006 / Accepted: 15 February 2008 / Published online: 27 March 2008
� Springer Science+Business Media, LLC 2008
Abstract We consider the extent to which the Mackenzie
Valley Resource Management Act (MVRMA) provides an
opportunity for deliberative democracy to emerge within
the context of resource management in Canada’s North.
The focus is on the extent to which the tenets of deliber-
ative democracy are exercised in the environmental
assessment (EA) of the Snap Lake diamonds project. Data
collection included semi-structured interviews with
assessment participants, and a review of documentation
surrounding the EA process, and the case study. Results
combined four principles of deliberative democracy: gen-
erality, autonomy, power neutrality, and ideal role taking.
The EA conducted under the MVRMA can serve as a
deliberative process, as illustrated by opportunities for
dialogue, access to different perspectives, and learning
outcomes. However, many of these positive results occur-
red through nonmandated technical sessions. The absence
of participant funding also limits the deliberative potential
of the MVRMA.
Keywords Deliberative democracy �Environmental impact assessment � Learning �Northwest Territories (Canada) � Diamond mining
Introduction
Natural resource management lies at the nexus of human-
environment interactions. Consequently, there is consider-
able attention by the public, practitioners, and academics
on establishing management processes that minimize con-
flict while recognizing sustainability goals (e.g., Duinker
and others 2003; Gibson 2006; Mitchell 2002). The types
of management processes that are being tested tend to be
inclusive and open, which is consistent with the broader
trend toward more participatory environmental governance
(Dorcey 2004; Parson 2001). Parkins and Mitchell (2005)
indicate that this interest in more transactive and deliber-
ative approaches to decision making is ‘‘fueled by
increasing scientific complexity and uncertainty, along
with a lack of social consensus about how natural resources
should be managed.’’ Consequently, governments are
seeking more active participation in selected areas of
natural resource management.
The trend toward more active participation in issues of
resources management is illustrated through a variety of
initiatives arising from governance bodies, academia, and
civil society. For example, the adoption of the Aarhus
Convention on Access to Information, Public Participation,
and Access to Justice in Environmental Matters by the
European community has resulted in changes to European
law (Hartley and Wood 2005). Major financial institutions
involved in funding resource development also stipulate
public participation as one aspect of the lending process
(Pring and Noe 2002). There is also a move to include
participation as a human right.
In the natural resource and environmental management
context, environmental impact assessment (EIA) has a
significant history of including people in decision processes
(Petts 1999; Sinclair and Diduck 2005; Wood 1995). In
P. Fitzpatrick (&)
Department of Geography, University of Winnipeg, 515 Portage
Ave., Winnipeg, MB, Canada R3B 2E9
e-mail: [email protected]
A. J. Sinclair
Natural Resources Institute, University of Manitoba, Sinnott
Building, 70 Dysart Rd., Winnipeg, MB, Canada R3T 2N2
B. Mitchell
Department of Geography, University of Waterloo, Waterloo,
ON, Canada N2L 3G1
123
Environmental Management (2008) 42:1–18
DOI 10.1007/s00267-008-9098-2
fact, public participation has long been recognized as a
cornerstone of EIA process. In support of this, organiza-
tions, such as the International Association for Impact
Assessment, now have subgroups dedicated to improving
these participatory practices. There is also a wealth of lit-
erature, spanning both the academic and public genres,
which include, among others, guidance material about how
to get involved in EIA, written by state, public, and cor-
porate actors. The range of activities designed to strengthen
public participation illustrates the importance of this aspect
of resource management.
Deliberative democracy provides one lens through
which to examine the characteristics of the civil space
created to encourage participation, the decisions reached
through participatory processes, and the learning outcomes
associated with the participation. Grounded in the theory of
communicative action, deliberative democracy is con-
cerned with repoliticizing the public sphere to encourage
different publics to become more actively involved in
political decisions (Dryzek 1990). Deliberative democracy
is ‘‘based on criticisms of more episodic forms of demo-
cratic participation, where involvement is limited to voting
and where public deliberation is severely limited to issue
sound bites and popularity contests’’ (Parkins and Mitchell
2005). It thus advocates interaction among a broad range of
participants, with the expectation that by doing so the
decision-making process, and subsequent policy decisions,
will be more legitimate and rational (Abelson and others
2003; Baber 2004; Enslin and others 2001). Beyond con-
tributing to policy decisions, a deliberative processes is
expected to foster individual and social learning, as par-
ticipants are exposed to a range of different perspectives,
and engage in dialogue (Welton 2001). Thus, deliberative
democracy focuses on development both in the public
sphere and by individuals.
The Northwest Territories is one region in Canada in
which public participation has been identified as a key
component of decision-making surrounding resource
management. Our purpose here is to consider the extent to
which the Mackenzie Valley Resource Management Act,
1998 c.25 (MVRMA) provides an appropriate structure for
deliberative democracy to emerge within the context of
resource management in Canada’s North through the EIA
process mandated by the Act.
The Mackenzie Valley Resource Management Act
(MVRMA)
Emerging from the resolution of three comprehensive land
claims in the region, the MVRMA is designed to ‘‘create a
system of land and water management’’ (preamble) ‘‘with
the intention of providing northerners decision-making
participation and responsibility in environmental and nat-
ural-resource matters’’ (MVEIRB no date). Thus, the
MVRMA establishes structures and processes designed ‘‘to
foster greater collaboration among key stakeholders in the
region’’ (Armitage 2005b). The Act creates six public
boards to oversee different resource management pro-
cesses, which includes land and water management, EIA,
and environmental monitoring and auditing (Under the
MVRMA, EIA describes the assessment process in its
entirety, whereas an EA is a specific stage in the
assessment).
The MVRMA was enacted in 1999, and expectations
were high. As observed by Gwich’in Tribal Council Pres-
ident, Nerysoo (1999), ‘‘For the Gwich’in, it is quite clear
that the intention of the legislation is to ensure that we have
participation in the decision-making processes that affect
the environment, that affect resource development, that
affect people and the way in which we develop land gen-
erally, and resources as well.’’
Indeed in the first audit of the legislation, completed in
2006, participation—in particular ‘‘the proactive nature of
community involvement and the degree to which public
input can influence the process,’’—is recognized as a
unique aspect of this resource management regime
(SENES Consultants Limited 2006). Furthermore, a pre-
liminary analysis of EIA under the Act concluded that it
had several innovative structures necessary to foster col-
laboration among participants, and provide for learning
(Armitage 2005a).
Deliberative Democracy and EIA
‘‘In its simplest terms, deliberative democracy refers to a
conception of democratic government that secures a central
place for reasoned discussion in political life,’’ (Cooke
2002). A deliberative process is situated in a public space,
where government and citizens, expressing a range of ideas
about an issue, meet and engage in dialogue, with the
idealized goal of achieving mutual understanding and
consensus (Dryzek 1990; Habermas 1984, 1987). A
deliberative process emphasizes discourse among people to
contribute effectively to decisions that affect them. While
discourse is a central design characteristic, advocates
suggest a deliberative approach benefits both the decision-
making process and outcomes (Cooke 2002; McGregor
2004). Public deliberation is viewed to educate citizen
participants, empower communities, result in fairer par-
ticipatory processes, strengthen the quality of the decisions,
and result in decisions that reflect modern social norms.
A deliberative process is governed by three sets of
‘‘rules’’, termed universal pragmatics (Habermas 1990;
Wiklund 2005):
2 Environmental Management (2008) 42:1–18
123
• logical-semantic rules necessary for individual com-
municative competence, which stipulate, for example,
that individuals should not contradict themselves,
• procedural rules that govern interaction among partic-
ipants, termed the theory of argumentation, which
identify four speech acts appropriate for debate, and
• process characteristics, which describe the ideal speech
situation necessary for noncoercive debate and (ulti-
mately) consensus among participants, termed the ideal
speech situation.
While there is no ideal model of deliberative democracy,
those presented in the literature draw on these rules
(communicative competence, the theory of argumentation,
the ideal speech situation) to evaluate the deliberative
potential of governance (Palerm 2000; Webler and others
1995; Wiklund 2005).
Consistent with the basic element of deliberative
democracy, namely including the public in governance
activities, all EIA legislation includes some requirement for
public participation, meant to achieve more informed
decision making (Petts 1999; Sinclair and Diduck 2005;
Wood 1995). The structures for deliberation encouraged by
deliberative democracy provide ‘‘a concise and general
summary of the requirements cited in [EIA] research for
impact assessment to achieve its analytical potential without
stunting democratic participation’’ (Baber 2004). However,
as observed by Wiklund (2005), the true deliberative
potential of EIA may rest not in opportunities for partici-
pation outlined by legislation or policy, but rather in the
flexibility of the institutions implementing these programs
to create more opportunities for interaction with the public.
A growing body of research evaluates EIA, and the
participatory aspects of EIA processes, based on criteria
derived from communicative action and deliberative
democratic tenets (Palerm 2000; Petts 2003; Webler,
Kastenholz and Renn 1995; Wiklund 2005). Each approach
focuses on the EIA process, drawing upon universal
pragmatics as the foundation for considering the delibera-
tive nature of EIA.
Deliberative Democracy and Learning
As noted above, deliberative democracy is concerned with
more actively involving the public in the political arena.
One consequence of more active participation is learning,
perhaps best described in this context as ‘‘the development
of individuals in a positive and coordinated man-
ner,’’(Webler, Kastenholz and Renn 1995). As people
interact in the public sphere, they are exposed to different
opinions, ideas, and evidence, among others, which provide
an opportunity for learning. Thus, participation in delib-
erative processes ‘‘improves the moral, practical or
intellectual qualities of those who participate: it makes
them not just better citizens—though clearly this is cru-
cial—but also better individuals’’ (Cooke 2002). Despite
these relationships, the role of learning is often underrep-
resented in the analysis of deliberative democracy (Morrow
and Torres 2002).
While a number of authors, including Webler, Kasten-
holz and Renn (1995), Palerm (2000), Poncelet (2001), and
Barabas (2004), recognize that when people are involved in
a deliberative process, such as EIA, learning may ensue.
Results presented in these evaluations focus on the process,
rather than outcomes. To more fully understand the
learning process and outcomes associated with a delibera-
tive process, we turned to transformative learning.
Transformative learning is a framework of adult learn-
ing and education with roots in the theory of
communicative action (Habermas 1984, 1987) and critical
pedagogy (Freire 1973). Learning ‘‘involves making a new
experience explicit and schematizing, appropriating, and
acting upon it,’’ (Mezirow 1991). Discourse surrounding
transformative learning centers on how to encourage
learning so an individual’s perceptions and consciousness
can be altered as that person is critically engaged in dis-
cussion. The overarching goal is to ‘‘help adults realize
their potential for becoming more liberated, socially
responsible, and autonomous learners’’ (Mezirow and
Associates 2000).
In the course of daily life, adults engage in activities that
must be understood in order to ensure appropriate and
effective action. In the act of providing a coherent frame-
work through which to understand an experience, one
confers meaning to the experience (Mezirow and Associ-
ates 2000). Learning, then, is the ‘‘process of using a prior
interpretation to construe a new or a revised interpretation
of the meaning of one’s experience as a guide to future
action’’ (Mezirow and Associates 2000). This process
results in revisions or reconstructions to the individual’s
frame of reference.
Rational discourse provides a medium through which
learning is promoted and developed (Taylor 2000). Thus,
understanding the conditions of the potential learning
activity is an important aspect of the analysis (Mezirow
1991; Sinclair and Diduck 2001). Learning is undertaken
by individuals who are engaged in dialogue, such as that
provided through deliberative democracy. In this way,
transformative learning is strongly influenced by the social
context in which it is undertaken (Jarvis 1987; Merriam
and Caffarella 1999). In doing so, transformative learning
builds on the social, situated nature of deliberation.
‘‘Knowledge is built together in a community of mutually
understood values and principles. This acknowledges
deliberation as a change process, one that invites each party
to the deliberation in a dynamic, interconnected way that
Environmental Management (2008) 42:1–18 3
123
moves beyond bargaining, compromise of consensus’’
(McGregor 2004).
A small, but growing, set of literature draws on trans-
formative learning as a framework for understanding
opportunities for adult development as they arise from
participation in EIA (Diduck 2001, 2004; Diduck and
Sinclair 1997; Fitzpatrick and Sinclair 2003; Sinclair and
Diduck 2001). This literature evaluates the learning envi-
ronment against conditions that foster transformative
learning, and discusses learning outcomes associated with
participation in EIA. Thus, learning can be an important
criterion through which to judge the success of participants
to adopt the attitudes necessary to undertake a deliberative
process.
Deliberative Democracy, EIA, and Learning
We adopted Wilkund’s (2005) framework for evaluating
the deliberative potential of the MVRMA, as facilitated
through EA. The framework was adopted after the empir-
ical research was completed. Although this may be
problematic in some instances, it was not in this case
because we had also used theory related to communicative
action and EIA process in developing our survey. This
framework contains four principles (Wiklund 2005):
• Generality: All those affected, or at least their interests,
shall be included.
• Autonomy: Everyone included shall be granted the
right of effective participation.
• Power neutrality: Distortions related to administrative,
economic and cultural power must be neutralized to
ensure that only the ‘‘forceless faces of the better
arguments’’ affect the outcome.
• Ideal role taking: Participants must adopt attitudes of
reciprocity and impartiality.
This framework emphasizes the political origins of delib-
erative democracy over those grounded in the rational
planning approach (such as Webler and others 1995;
Petts 2003), thereby providing ‘‘a democratic theoretical
foundation for deliberative E[I]A’’ (Wiklund 2005). Fur-
thermore, although learning was not originally considered
as part of this framework, it can readily be included as part
of the analysis.
We implemented the framework by establishing opera-
tional questions (Table 1). These questions are modified
from those originally posed by Wilklund (1995) for the
purpose of clarity, and to ensure that they strongly relate to
the literature regarding transformative learning (e.g.,
Mezirow 1991) and EIA (e.g., Petts 2003; Webler 1995), in
addition to deliberative democracy (e.g., Dryzek 1990).
These modifications are most clearly illustrated with
respect to the criterion of ideal role playing. The focus of
our inquiry changed from evaluating how the attitudes of
participants are reflected in specific actions (e.g., are the
participants listening and speaking sincerely?) to learning
outcomes. We chose this approach for two reasons (i) the
difficulty of trying to assess attitudes and whether they are
reflected in a decision, and (ii) the importance established
in the literature of learning as an outcome of deliberative
decision-making processes. Our approach embeds consid-
eration of individual and social development in the analysis
through consideration of the learning outcomes. We con-
sider if the participants leaned as a result of this process,
and what qualities of the process contributed to this
learning.
Methods
This study was qualitative, grounded in a critical social
science approach. Data surrounding the EIA process in
general were collected from the legislation, guidelines
prepared by the Mackenzie Valley Environmental Impact
Review Board (MVEIRB), and academic literature. Criti-
cal data related to the case study were collected from four
key sources:
Table 1 Theoretical principles (Wilkund 2005) and operational questions
Principles Operational questions
Generality: All those affected, or at least their interests, shall be included Was the EA open to interested parties?
Did participants represent a variety of interests?
Autonomy: Everyone included shall be granted the right of effective participation How was the public engaged in the EA?
Power neutrality: Distortions related to administrative, economic and cultural power must
be neutralized to ensure that only the ‘forceless faces of the better arguments’ affect the
outcome
Did the EA provide resources to ensure alternative
perspectives were presented?
Were steps taken to address the cross- cultural
context of the EA?
Idea role taking: Participants must adopt attitudes of reciprocity and impartiality Did participants learn as a result of the EA?
What qualities of the process best facilitated
learning?
4 Environmental Management (2008) 42:1–18
123
• EA documentation (recall that an EA is a specific stage
in the EIA process under the MVRMA),
• Media coverage,
• Semi-structured interviews with assessment partici-
pants, and
• A post hoc analysis of the EA commissioned by the
MVEIRB.
Documentation surrounding the EA was compiled from the
public registry, which spans 22 volumes. This material,
including the impact statement, information requests (IRs),
technical session minutes, hearing transcripts, and corre-
spondences, were reviewed with reference to key
constructs related to participation and learning. Many of
the quotes that follow come from these data. Media
coverage related to the EA prepared by the Canadian
Broadcasting Corporation and News North Services was
collected from the press websites. Papers spanning a period
between June 1999 and July 2004 were viewed on-line or
in hard copy at the Yellowknife Public Library.
Semi-structured interviews were completed in August
2004 with 14 assessment participants, representing two
levels of government, the MVEIRB, the proponent, and
nongovernment organizations. Purposeful, stratified sam-
pling was used to ensure that participants were actively
involved, and represented each type of organization
involved in the assessment (Table 2). Participants were
identified from assessment documentation, and ones with
active involvement in key stages of the EA (including
scoping, IRs, technical sessions, and hearings) were pri-
oritized for interviews. Interviews, lasting up to
120 minutes, were tape recorded and transcribed. Partici-
pants were initially contacted by telephone or email, and
subsequently were interviewed at their organization.
A study conducted by the MVEIRB following the Snap
Lake EA served as a fourth source of data. Released in
February 2005, the intent of this study was to improve the
effectiveness and efficacy of the EA process. The MVEIRB
sought input from assessment participants through written
surveys and interviews (conducted by independent con-
sultants). Board input was sought during two separate
workshops. Where appropriate, recommendations from this
report are included in the discussion.
Data analysis relied on the theoretical principles of
deliberative democracy, already described above, to develop
a preliminary list of codes to index data (Bernard 1994).
NVivo, a qualitative analysis software, was used to organize,
sort, and code themes (QSR 1999–2002). This software
provided a one-window approach to formatting, cross-
referencing, indexing, and abstracting data (Huberman and
Miles 1994). It allows directly transcribed text to be put into a
database and then memos, codes, and families of codes can
be developed.
The validity of findings was protected through use of
two strategies: (i) triangulation and (ii) interview reliabil-
ity. Triangulation is meant to minimize research bias by
ensuring that findings reflect reality. Multiple sources of
data, found in the four datasets described above, were
considered with respect to each aspect of the framework—
each therefore was important to the data collection and
analysis phases. Second, draft findings were sent to
research participants for review. This was done to ensure
that participants’ views and experiences with the assess-
ment process had been correctly documented.
As noted elsewhere, a key issue surrounding the appli-
cation of deliberative democracy is the requirement to
balance the ideal of open participation against what Dryzek
(2001) terms the economy of participation, namely the
Table 2 Organizations involved as intervenors or directly affected parties in the EA of the Snap Lake project (MVEIRB 2003)
Government Community and aboriginal
government
Nongovernmental organizations Industry Public
INACa,b Yellowknive Dene First Nationb Canadian Arctic Resources
Committeea,bDe Beers Canada
Inc.a,bVarious
DFOa,b North Slave Metis Alliance NWT and Nunavut Chamber of Mines
NRCana,b Dogrib Treaty 11 Council World Wildlife Fund Canada—
Yellowknifeb
Environment Canadaa,b Lutsel K’e Dene First Nationa,b World Wildlife Fund Canada—
Toronto
Government of the Northwest
Territoriesa,bNorthwest Territory Metis Nation
Metis Nation, Raw-Edzo Local
#64
Dene Nation
a Attended July 20, 2001 meeting about the work planb Commented on assessment terms of reference
Environmental Management (2008) 42:1–18 5
123
plausibility of including all participants in each and every
decision affecting them (Davies and Blackstock 2005;
Marshall and Jones 2005; Parkins and Mitchell 2005;
Parkinson 2003). We accept the view that legitimacy can
be achieved through representative participants (Davies
and Blackstock 2005; Parkinson 2003). Deliberative
democracy is meant to engage the public, or their repre-
sentatives, in decision making, and the participants
identified in this study represented different organizations
involved in the EA (including the MVEIRB, directly
affected parties and intervenors). This emphasis was
deliberate; while the EA process invites the general public
to be involved, the overwhelming majority of participants
in the Snap Lake process were affiliated with different
organizations as employees, consultants, members, or
experts. For example, during the technical sessions and
hearings, the documentation identifies many elders both
observing and participating in the event. However, when
speaking, the elders spoke as members of their community,
and thus were acting as representatives of their govern-
ments. Furthermore, these community governments, in
submitting written reports, make it clear that their sub-
missions were on behalf of their constituency, and that
consultation had been undertaken with members. However,
here we do not address the nature of these relationships,
e.g., how organizations consulted with their members.
The Snap Lake Project
The Snap Lake project was the third diamond development
in the Slave Geological province to be subject to an
assessment, but the first to be reviewed in its entirety under
the MVRMA. This project involves the construction and
operation of a diamond mine located 220 km northeast of
Yellowknife, at the headwaters of the Lockhart River
drainage system (Fig. 1). After undergoing a preliminary
screening, the project was subjected to a more rigorous
assessment, termed an environmental assessment (EA). As
summarized in the assessment recommendation, the project
underwent an EA due to significant public concern
regarding ‘‘cultural well being, lack of environmental
assessment, net effects on government, and issues of sus-
tainable development,’’ (MVEIRB, public registry, May
23, 2001). Against that context, we examined the EA
process for Snap Lake with reference to the principles of
deliberative democracy.
Generality
This principle provides a lens to examine the participatory
nature of the EA process. In other words, the principle
considers if the public is provided opportunities to become
involved in the decisions that affected them, as well as the
representative nature of those who become involved in the
review.
Seventeen organizations and many individuals partici-
pated in the EA of the Snap Lake project (Table 2). All of
the organizations had previously been involved with an EA
of a diamond mine in the Northwest Territories.
All interested individuals and organizations were given
an opportunity to be involved in the EA; the Board granted
all requests for intervenor or directly affected status,
resulting in the list of participants identified in Table 2.
Fig. 1 The Snap Lake diamond
mine is located northeast of
Yellowknife, Northwest
Territories, Canada (Map credit:
Weldon Hiebert, University of
Winnipeg)
6 Environmental Management (2008) 42:1–18
123
However, this list of participants differs significantly when
compared to those involved with previous diamond-based
development. The total number of participant organizations
decreases from 50 in the first diamond-based assessment
(BHP Environmental Assessment Panel) to 17 in the Snap
Lake project (Table 3). The most significant decreases
relate to nongovernmental organizations (such as the
Roman Catholic Dioceses of Mackenzie, the Status of
Women Council, and the Canadian Nature Federation), and
community and Aboriginal governments. However, the
number of intervenors or those with directly affected status
do not accurately reflect the number of organizations which
were kept informed of all EA information by being copied
on the public registry (see information management
below).When comparing the distribution list regarding the
Snap Lake EA with participant organizations from the
previous diamond-based EAs, three categories of partici-
pant organizations (government, industry, and community
and Aboriginal government) level off with the same core
group of participants, while the fourth category, nongov-
ernmental organizations, experiences a sharp decrease
(again with a core group of participants). Organizations
that decided not to participate more actively were not
consulted in our study so we do not have data regarding
their specific reasons.
In situations where organizations choose not to partici-
pate in a decision-making process, some practitioners and
researchers consider whether the interests of the nonpar-
ticipants are adequately reflected in the decision (Davies
and Blackstock 2005; Dryzek 2001). While considering if
this aspect was beyond the scope of this research, one
measure of how well interests of nonparticipants were
reflected in the Snap Lake case could be that none of the
previously-active participants challenged the assessment
decision through litigation, which is usually cited as the
ultimate remedy for public engagement in resource man-
agement decisions and an approach practiced in Canada
(Zillman and others 2002).
Autonomy
This principle indicates a need to explore when and how
the public participates in the process. It considers how the
process fosters or hinders the ability of participants to
engage in argumentation at different points of the assess-
ment (Abelson and others 2003; Wiklund 2005).
Participation in the EA of the Snap Lake project was
encouraged through:
• inviting written submissions related to the draft terms
of reference and EA work plan,
• inviting written submissions regarding the conformity
of the impact statement to the guidelines,
• inviting written questions and answers regarding the
impact statement, called IRs,
• facilitating oral dialogue during 10 days of technical
sessions,
• preparing written technical reports surrounding the
potential impacts of the project,
• facilitating oral presentations, supported by written
material during 5 days of hearings, and
• maintaining a public registry about the project.
Table 4 lists key provisions for adequate participation, as
established by Sinclair and Diduck (2005) and compares
these provisions with opportunities for participation in an
EA established by the MVRMA, assessment guidelines
established under the Act, and as undertaken for the Snap
Lake EA. As illustrated in Table 4, the deliberative
potential of assessment is often ‘‘hidden’’ because legisla-
tion establishes minimum requirements and individual
cases often go well beyond the minimum, as in this case,
when large projects are being considered (Wiklund 2005).
Participants identified four key issues that had both
positive and negative consequences for public participa-
tion: the absence of public scoping sessions, the presence
of technical sessions, the way EA information was man-
aged, and hearings.
Scoping
Scoping is the process of determining what should be
included in the terms of reference for the developer’s
assessment report. Although not specified in the MVRMA,
public participation in EA scoping traditionally includes
both written comments and community meetings facilitated
by the MVEIRB. The draft work plan and terms of refer-
ence for the developer’s assessment report for the Snap
Lake project were released on July 25, 2001, and over
Table 3 Categories of organizations involved in diamond-based assessments in the NWT
Government Community and aboriginal government Nongovernmental organizations Industry
BHP NWT Diamond Project 6 17 23 4
Diavik Diamond Project 7 8 10 3
Snap Lake Projecta 5 (1) 7 (11) 4 (3) 1 (2)
a The number in brackets represents organizations included on the distribution list but not actively involved in the EA
Environmental Management (2008) 42:1–18 7
123
30 days, the public was invited to submit written
comments.
The lack of public scoping meetings was identified as a
concern by one NGO and one Aboriginal government
organization, which expressed reservations at a public
meeting held just prior to the release of the work plan and
terms of reference (MVEIRB, public registry, July 21,
2001), and through a formal request submitted to the
MVEIRB (public registry, August 21, 2001, and August
27, 2001). As summarized by the Canadian Arctic
Resources Committee, ‘‘Northern communities rely on
personal relationships and communications, often where
English is not the preferred language’’ (Kevin O’Reilly,
public registry, August 21, 2001). Thus, using written
communication as the only form of public input during an
important stage of the assessment process decreases the
ability of interested parties to become involved in the
assessment.’’
Despite this appeal, the MVEIRB (public registry,
September 18, 2001) decided against holding public
scoping meetings. This decision was influenced by three
factors: (i) prior experience with recent diamond-based
development in the same region (which provided a foun-
dation for developing the draft terms of reference for the
Snap Lake project), (ii) the observation that the board
would provide opportunities for public comment at future
points in the EA, and (iii) the feedback would be provided
through the Terms of Reference and Work Plan.
As noted in Table 2, seven of the ten participant orga-
nizations and one member of the public submitted written
comments regarding the draft work plan and terms of ref-
erence for the review. Numerous specific requests were
addressed in the revised terms of references, including:
• a request for a revised approach to the spatial scope of
assessment (World Wildlife Fund, Yellowknife),
• the need to discuss ecologically representative areas,
specifically in the wildlife and wildlife habitat section
(World Wildlife Fund, Yellowknife),
• a discussion of forecasting models in the cumulative
effects section (World Wildlife Fund, Yellowknife),
• the use of milestone days rather than calendar days in
the timeline summary (NRCan),
• a desire to have information about the company’s
corporate history in the developer’s assessment report
(Yellowknife Dene First Nation),
• changes in the approach to traditional knowledge
(Lutsel K’e Dene First Nation),
• a request for a discussion around diamond sorting and
marketing diamonds (Government of the Northwest
Territories),
• specific additions to identified environmental impacts
of interest, including hazardous materials, air quality
and climate, terrain, water quality and quantity, aquatic
habitat, cultural resources, land and resource use,
economy, cumulative impacts, abandonment and res-
toration and follow up programs (MVEIRB 2001),
• the addition of two environmental impact topics, the
regulatory regime and corporate compliance (MVEIRB
2001), and
• general changes in document formatting (MVEIRB
2001).
Comments not addressed by the revised terms of reference
include the request by Environment Canada for clarifica-
tion of MVEIRB’s position on compensation for potential
negative impacts, and a discussion of how significance is
Table 4 Opportunities for public participation in EA under the
MVRMA legislation, guidelines, and as provided for in the Snap Lake
EA
EA stage Legislation Guidelines Case
study
Notice
Start of EA 126(5) s 3.5 4
Board site visit 4
Hearings s 3.15 4
Announcement of
authorizations
4
Public comment
Scope (draft terms of reference and
work plan)
Written comments s 3.9a4
Public sessions
Conformity analysis s 3.12b4
Technical review
Ad hoc technical meetings 4
Technical sessions s 3.13c4
Information requests s 3.14 4
Technical review s 3.13 4
Pre hearing conference s 3.15c4
Hearings
Formal hearings s 3.15c4
Community sessions s 3.15c
Access to information
Public registry s 3.7 4
Public record NAP NAP
EA decision
Distribution of decision s 3.16 4
Participant funding
NAP means the step could not be accessed by the publica Although opportunities for public participation are identified in the
guidelines, these steps may be completed in camerab While these steps are usually completed in camera, they may be
open to the publicc These steps are discretionary
8 Environmental Management (2008) 42:1–18
123
determined by the MVEIRB with respect to public concern
(Yellowknife Dene First Nation).
Although scoping was not conducive to Aboriginal
participation, the panel was diligent in addressing the
written comments, as illustrated by changes to the terms of
reference, and absence of continued conflict over the terms
of reference throughout the review. Indeed, a post-assess-
ment survey conducted by the MVEIRB identified the
incorporation of participants’ needs in the terms of refer-
ence as one strength of the review (MVEIRB 2005).
Technical Sessions
Technical sessions were an addendum to the standard
MVEIRB process. These sessions, held for 10 days in
December 2002, in Yellowknife, provided an opportunity
for the participants to meet with the proponent’s experts to
resolve outstanding issues prior to the submission of
technical analyses of the developer’s assessment report.
Technical sessions were open to the public, but transcripts
indicate that participants were affiliated (including a range
of members, consultants, experts, and employees) with the
intervenor and directly affected organizations.
Two days were allocated for each of the five different
themes: water quality, fish and fish habitat, wildlife, geo-
technical and socio-economic issues. At each session,
participants were invited to present concerns related to the
theme; experts, representing the different organizations,
then discussed the information available in the assessment
documentation, contrasted with findings in the literature. In
some cases, an issue required additional information than
what had earlier been provided. An issue was considered
resolved if those involved in the specific concern felt the
issue had been resolved. Minutes were prepared by session
facilitators (independent consultants hired by the
MVEIRB), and several months later session transcripts
were provided. While the board did not attend the technical
sessions, MVEIRB staff and technical consultants were
active participants, along with intervenors, directly affected
parties, and members of the general public. Furthermore,
before leaving the meetings, the Chair of the MVEIRB,
Gordon Wray, reviewed the process used to that point, and
set out the context for the technical sessions: ‘‘I strongly
encourage you to have an open and informal exchange and
to work your way through the agenda in a focused and
efficient manner (MVEIRB public registry, November 25,
2002).’’
Assessment participants identified the technical sessions
as a strength of the EA process (MVEIRB 2005). Sample
commendations, collected from interviews and the assess-
ment report included: ‘‘I think getting everybody into the
room for those 10 days was probably the most beneficial.
Just having open discussion’’ (Interview 1), ‘‘I would like
to see more of that type of process [e.g., technical sessions]
included in the Board’s procedures’’ (Interview 12), and
‘‘The technical session approach, where we had one-on-one
dialogue, you know, got to the bottom of the issues and
concerns in a much more pro-active and consultative way’’
(MVEIRB 2003).
As these comments indicate, participants believed that
the technical sessions allowed open discussions, and one-
on-one dialogue with proponents and decision makers
expected in a deliberative context. This was achieved in
part by allowing a significant amount of time to discuss
different issue areas, by having trained facilitators leading
the sessions and through those facilitators using approaches
that contribute to dialogue, such as break out groups. At the
end of the technical session, people were left with a clear
understanding of what issues had been resolved and which
still required attention.
Although these sessions were successful, participants
still provided suggestions about how to strengthen this part
of the process:
• ensure that participants have clear direction on the
purpose of the technical sessions (namely to resolve
outstanding issues). Session facilitators should ensure
that issues are clearly scoped (see next bullet), and
participants are provided with ample opportunity to
resolve issues (Interviews 1, 6, 7),
• ask intervenors to prepare ‘‘draft’’ or ‘‘interim’’ tech-
nical reports to focus the process on ‘‘outstanding
issues’’ prior to the technical sessions (MVEIRB 2005),
• develop a system to track issues discussed during break
out sessions (Interview 12),
• provide outside facilitation for break out sessions
during the technical sessions (MVEIRB 2005), and
• notes should be available for editing by participants,
and become part of the public registry and record
(MVEIRB 2005).
In the end, participants liked the technical sessions because
they provided an opportunity for all involved, including the
public, to become actively involved in an iterative dialogue
focused on resolving issues. For many participants, this
was unlike other experiences they had with hearings or
boards in which participants present their cases, a few
questions may be asked, and the information given is later
judged against the variety of alternative perspectives
presented. In this case, the participants actually were able
to discuss the alternative perspectives.
And when you get to the technical sessions where you
have the proper people there to discuss issues you get
resolution so much quicker, and you can see where people
stand on the issues, and as a whole, you can get all the
parties involved, and I see that as being much more
effective (Interview 6).
Environmental Management (2008) 42:1–18 9
123
Information Management
Ready access to information provided by proponents, and
to any comments offered by participants and regulators, is
essential for meaningful participation (Sinclair and Diduck
2005). There must be opportunities for the timely exchange
of information among all parties. A registry or repository
system is the basic means of public access to information
used in most Canadian jurisdictions. Such registries are
usually held in libraries as well as in other public buildings
to facilitate orderly access to the information. Some juris-
dictions provide Internet access (or partial access) to their
public registries.
The MVRMA makes provision for a public registry, and
states that the registry ‘‘is a complete set of documents
related to the environmental assessment.’’ It includes
‘‘documents from the preliminary screening file, plus the
Terms of Reference, the Developer’s Assessment Report,
all information requests, rulings, technical reviews, letters,
Reasons for Decisions, and any other documentation’’
(MVEIRB 2001). There was one, central location for the
Snap Lake project public registry, in the Review Board
office in Yellowknife. Much of the documentation,
including rulings, transcripts, presentations and an up-to-
date table of contents, was also posted on the MVEIRB
website, http://www.mveirb.nt.ca/.
For the Snap Lake project, MVEIRB staff forwarded all
material on the public registry to key contacts, such as
Band Managers or Wildlife Management members, in
affected communities, including groups not identified as
intervenors or directly affected parties. This resulted in the
creation of ‘‘satellite’’ registries located in communities
potentially affected by the development, and in organiza-
tions active in the review process. To ensure that the
records were consistent, and up to date, MVEIRB staff
periodically sent out a revised table of contents, against
which participants could compare their satellite documen-
tation information.
While the public registry appears to provide a compre-
hensive record of EA documentation, during the Snap Lake
EA the participants learned that the public record—the set
of documents on which the panel bases its decisions—
differed from the material on the public registry. The
public record maintained by MVEIRB included informa-
tion not found on the public registry that was deemed to be
in the proprietary interest of the proponent, as well as
correspondence between the MVEIRB and its staff.
This lack of harmony between the two sets of records
was of particular concern to the North Slave Metis Alli-
ance. It expressed dissatisfaction with being unable to
review documentation provided to the MVEIRB by its staff
or consultants (e.g., Janet Hutchison, public registry, Sep-
tember 17, 2002, Kris Johnson, public registry, April 9,
2003, May 15, 2003, North Slave Metis Alliance, public
registry, April 9, 2003), particularly regarding documen-
tation surrounding assessment activities not observed by
the MVEIRB (e.g., the technical sessions) or by the public
(e.g., the MVEIRB visit to the project site). Ultimately, the
MVEIRB (public registry, July 9, 2003) ruled against this
request, observing that as an administrative tribunal, it was
inappropriate for the board to comment on the fairness of
its processes and noting that any remedy would have to be
through the court system.
A second comment related to the need to improve
mechanisms to track issues. If a purpose of the EA process
is to narrow the focus of the review to key areas of interest,
then there has to be an efficient way to look up key issues,
and determine the status of discussion (e.g., resolved,
outstanding, on-going discussion, key parties, etc). Partic-
ipants advocated a nonpartisan system for recording
assessment issues, to make documentation more user
friendly. Thus, participants promoted the development of a
database designed to track efforts to resolve issues
throughout the assessment (MVEIRB 2005).
The need for information tracking takes on particular
importance when IRs become part of the review process.
As noted above, IRs, involving multiple series of written
questions and answers designed to clarify and strengthen
information provided in the developer’s assessment report,
were a new step in the assessment process. Three rounds of
IRs occurred during the Snap Lake process, resulting in
433 IRs issued by the Board, which required responses to
944 questions. This process, then, generated a significant
body of information. Nevertheless, all interviewed partic-
ipants indicated that this component of the review process
needs improvement: ‘‘IR rounds, although beneficial, took
a long time, and you did not really get the answer you
wanted in a quick time turn around’’ (Interview 1); ‘‘There
was probably another 5000 pages of information printed,
thereby negating the whole accessibility of information to
all’’ (Interview 2); ‘‘[IRs] can be an effective tool if it is
used properly, and I think it was kind of—it became a new
tool in this process, not everyone was familiar on how it
would be used, but it kind of became overwhelming, and
complicated things a bit’’ (Interview 6); one participant
also observed that having the IRs issued through the
MVEIRB challenged the integrity of the requests, as some
questions were either incorrectly reworded or never for-
warded (Interview 7).
Many participants felt that IRs should be approached
with caution, as technical issues are often resolved more
quickly and thoroughly through discussion, rather than
through written responses. Although none of the partici-
pants suggested that IRs should be eliminated, numerous
ways to strengthen this component of the review were
suggested. These included the need to:
10 Environmental Management (2008) 42:1–18
123
• create opportunities for participants to narrow the scope
of the review earlier in the process (i.e., before the
technical review and IR processes). If the review is
focused on key issues of the concern to the assessment
community, the number of IRs will likely decrease
(Interview 5),
• limit the IR process to one, or at most two rounds,
• create blocks of time for the IR process, so that
deadlines for submitting questions do not occur before
participants have received and have an opportunity to
review responses to previous questions,
• provide resources for organizations to participate in the
IR process (see discussion below about participant
assistance),
• develop a template for information requests (MVEIRB
2005),
• provide a way to track issues as they change through
the IR process, and
• reduce editing of IRs by the MVEIRB (2005).
As these comments depict, participants had access to
significant amounts of information surrounding the Snap
Lake project, an important precondition for allowing
informed dialogue about the assessment in a deliberative
process. Results, however, support recent research sug-
gesting the next step in information management is to
ensure that data are presented in an efficient, readable
manner (Diduck and Mitchell 2003).
Hearings
The EA ended with five days of hearings, held in Yel-
lowknife between April and May 2003. As with the
technical sessions, hearing days were allocated by theme.
Daily activities included presentations and cross-examina-
tion by all directly affected parties, intervenors, the Board,
and the public interested in that topic. In this respect, the
hearing functioned much like other EA hearings in Canada,
parties presented their case to the Board and some cross-
examination of the evidence presented ensued. The
MVEIRB sat primarily during business hours. However,
the time frames were extended, where necessary, to ensure
that discussion related to the topic at hand was complete.
Furthermore, the Thursday session was extended into the
evening to provide elders with an opportunity to share their
thoughts with the MVEIRB. Hearings were simultaneously
translated into Chipewyan and Dogrib.
Although many participants found the hearings to be a
less effective mechanism for resolving assessment issues
than the technical sessions due to the lack of opportunity to
dialogue with other intervenors, all realized the importance
of this activity (Interviews 1, 2, 5, 12).
And I think often that an iterative consultation would be
more productive in a lot of ways than the formal procedural
thing. But of course then you get into legal things, and
again, another big challenge is to minimize the formality
and legality of the process while still making it so you
people can’t lie, and that they are being held into account
for what they said, and that sort of thing (Interview 12).
Hearings provide participants with one last opportunity
to discuss issues, although, as noted by two participants,
some became engaged in posturing because of the presence
of the Board. But, hearings are a significant part of process,
in that oral discussion is a key component of First Nations’
cultures, and hearings come closest to reflecting this
emphasis on dialogue: ‘‘[Y]ou have everyone sitting there
and you can see everybody’s faces, and you can put a face
to each company and each agency and board member,
whatever. And you can go and talk to them face to face and
say ‘This is our concern’’’ (Interview 31).
Although efforts were made to make the hearings
accessible to participants (simultaneous translation, modi-
fied hours of operation), further modifications had to be
made as the hearing progressed. For example, a change was
made on the first day to provide elders with accessible
seating. Furthermore, while time was allocated for elders to
testify, because this was during an evening session, not all
people who wanted to speak were able to attend the pro-
ceedings. As noted by one participant, ‘‘they often put the
elder’s thing in an evening session—well, I am not sure
that that is always really fair to the elders, because not
many people will show up to listen to them’’ (Interview
12).
That the MVEIRB was somewhat flexible and made
efforts to accommodate the needs of its participants was
important to ensuring good outcomes. However, one rec-
ommendation from the MVEIRB’s post hoc analysis was to
meet ‘‘with elders to discuss their needs when participating
in the EA process’’ (MVEIRB 2005b). Suggested aspects
for discussion include seating arrangements and time of
day for meetings.
Power Neutrality
This principle considers how the process is designed to
ensure that participants are judged only on the strength of
their arguments. It considers the capacity of citizens to
become involved in the deliberative process, and how the
process works to address potential power inequities
(Wiklund 2005). Operational definitions for this criterion
focused on two administrative aspects traditionally used in
Canadian EA to minimize barriers: (i) equal participation
by all interested groups and (ii) ability to contribute to
evaluating arguments based strictly on merit. In the first,
the operational definition focuses on the resources provided
to ensure alternatives perspectives could be brought for-
ward through the process and therefore considered. In the
Environmental Management (2008) 42:1–18 11
123
second, we recognize there are multiple, culturally-based
ways of understanding the world, and many of these cul-
tural perspectives do not reflect the requirements of
Western social thought (see for example Berkes 1999; Ellis
2005; Kendrick and others 2005; Simpson 2000). Thus the
operational definition considers procedures undertaken to
respect the cross-cultural demographic of the Northwest
Territories, which include many different First Nations.
Participant Funding and Access to Alternative
Perspectives
Various researchers have noted the importance of partici-
pant (or intervenor) funding (e.g., Gibson 1993; Wood
1995), a view echoed by Canadian ENGOs. For instance,
the Canadian Environmental Network continues to advo-
cate a point they made some years ago that:
‘‘Effective participation by the public requires funding.
The disproportion of resources between proponents and the
public necessitates the establishment of an independent
funding body to provide adequate amounts of funding to
allow full and meaningful participation, at all steps, to
committed members of the public’’ (Canadian Environ-
mental Network-Environmental Planning and Assessment
Caucus 1998).
Participant assistance, when provided, is usually
reserved for large-scale EAs. In such cases, funding can
facilitate a more substantive dialogue by allowing partici-
pants to draw upon independent technical expertise related
to specific issues in the assessment (Lynn 2000; Lynn and
Wathern 1991). Funding can be used to prepare and par-
ticipate in scoping meetings, review draft assessment
guidelines, review the proponent’s EIS, and prepare and
participate in public hearings.
There is no provision for participant funding during an
EA under the MVRMA. Participants felt that this lack of
financial assistance limited the degree of public participa-
tion in the review process, as reflected in the following
comments: ‘‘and with De Beer’s Snap Lake, we couldn’t
afford, as a small organization, to intervene to the same
extent as we did with the other two projects. And it was
difficult to raise money; there was not participant funding’’
(Interview 3) and ‘‘to allow for better participation, you
need more money and more time’’ (Interview 10).
Without participant funding, some public organizations
were unable to conduct new research to help critique the
proponent’s data.
Despite the lack of financial capacity by organizations,
alternative perspectives were forwarded by some govern-
ment organizations during the EA. For example,
governments took an active, adversarial role in the EA; all
branches of government involved in the review—the fed-
eral and territorial governments, along with the
MVEIRB—believed their function was to challenge and
test assessment evidence (e.g., It is our job to ‘‘identify
issues and hash out issues’’ [Interview 6]). Thus, various
government agencies contracted independent technical
experts to review the documentation: ‘‘I would want to
compliment government for bringing forward the number
of technical experts... But more importantly, I think what
carried the De Beers Snap Lake process and made it more
rigorous, was the fact that the Board retained a whole raft
of technical experts, both on the socio-economic side, and
the environmental side, and that was absolutely key and
critical that they did that’’ (Interview 3).
One participant suggested that, in light of this govern-
ment function, participants do not need to hire independent
expertise to review the assessment material; to do so would
be a duplication of efforts. However, the majority of
research respondents did not share this opinion. Government
departments do not always complete an exhaustive, inde-
pendent review of EA material (see for example Fitzpatrick
2006). Furthermore, even if governments act as an inde-
pendent reviewer, the public may perceive that they are not
fulfilling this function, particularly given their participation
in the approval of resource projects. Consequently, partici-
pant funding strengthens the interactive policy-making
process by increasing the capacity of organizations to hire
independent technical advice.
A second source of material from alternative perspec-
tives was developed outside the MVEIRB environmental
assessment process. Baseline information about valued
ecosystem components was collected during a 5 year pro-
gram, managed by the West Kitikmeot Slave Society
(WKSS). This society was formed to oversee a research
program directed at creating baseline information to be
used for resource management in this region. During this
program, 19 projects conducted by independent researchers
were funded, covering issues ranging from local traditional
knowledge research to regional wildlife studies, at a
total cost of approximately eleven million dollars (David
Livingstone, personal communication, August 18, 2005).
Data collected through the WKSS were included in the
proponent’s development assessment report.
More closely tied to the Snap Lake project, however, was
an impact assessment, conducted by Lutsel K’e Dene First
Nation. Lutsel K’e is the closest community to the project.
In planning its approach to the review process, the com-
munity decided it wanted a more active role in the EA than
that of intervenor. It approached De Beers, and successfully
asked for funds for a community-based EA, based on tra-
ditional knowledge and history of the area. As noted by one
member of the community, ‘‘that report was provided to De
Beers, and it was included in its entirety, without De Beers
editing it, in their environmental assessment report—their
actual submission to the review Board.’’
12 Environmental Management (2008) 42:1–18
123
For some, the lack of participant funding negatively
affected the degree to which participants characterized the
Snap Lake EA as equitable. Some observed that, although
the process was open to all interested parties and was con-
ducted in a fair manner, the government and the proponent
have easier access to the process. Not only did these groups
have access to capital to fund participation, but also
employees of these organizations were paid to attend the
proceedings: ‘‘No [I do not think all interested parties had an
equal opportunity to be heard in the process], I think it was a
bit easier for government, because that is what they are here
to do. But for the public and the First Nations groups, they
had a difficult time with capacity, keeping up to speed on the
information, and the information requests back and forth’’
(Interview 1). In light of this perceived inequity, such par-
ticipants did not view the proceedings as equitable.
Cross Cultural Perspective
One type of power distortion prevalent in modern Canadian
society relates to ways of knowing. As noted above, there
are different ways of knowing, and there is a growing lit-
erature surrounding how to respect and address cross
cultural perspectives, particularly traditional knowledge,
within EIA (see for example Stevenson 1996, Usher 2000).
This issue was of particular concern in the Snap Lake EA,
situated in the traditional territory of the Lutsel K’e Dene
First Nation.
Ellis (2005) identifies a number of barriers affecting the
full and equal consideration of traditional knowledge in
resource management in the Northwest Territories, draw-
ing from the experiences of the Lutsel K’e Dene Nation.
Although he reviews a variety of top-down and bottom-up
approaches surrounding the collection and use of tradi-
tional knowledge, he concludes that full consideration is
hindered by significant, systematic barriers, including
communication, conceptual, and political barriers. Ellis
(2005) observes that ‘‘strategies used to foster traditional
knowledge at the community level have had some suc-
cess….however, often this empowerment occurs in the
broader context of the needs and expectations of Euro-
Canadian agencies and their decision-making processes’’.
As noted above, Lutsel K’e Dene First Nation submitted
a community-based developer’s report, based on traditional
knowledge, to the MVEIRB. However, at least one First
Nations’ participant questioned how this document was
considered in the EA process: ‘‘The first step was getting
De Beers to include [the LKDFN developer’s report] in
their environmental assessment report. So I think that was
fairly effective. Now the second step was convincing the
regulators, and all the other intervenors, that this is some-
thing valid to do. In fact, De Beers had a much better time
handling the results of that report than say [other agencies
who] just had no clue how to deal with that stuff’’ (Inter-
view 31).
This participant then suggested that the structure of the
proceedings naturally hinders participation. If some of the
public is not well versed in Western democratic institu-
tions, participation is limited: ‘‘The opportunity is provided
to participate...but that participation is conditional on
people being able to act like Western bureaucrats, and that
is the real problem’’ (Interview 31).
This observation reflects the critique from Habermas’
theory of communicative action that communicative com-
petence is a precondition for participation. If people are not
skilled in Western-based political and legal institutions,
can these frameworks of governance ever be used suc-
cessfully to negotiate the lifeworld? Transferred to this
case study, this question asks if systems for managing
environmental resources do not reflect the needs and
decision-making processes of the constituents of the Ter-
ritory, can they ever be equitable and effective?
In July, 2005, the MVEIRB released guidelines for the
incorporation of traditional knowledge in assessments,
which may address some of the concerns identified through
the Snap Lake EA (MVEIRB 2005a). These guidelines
identify procedural aspects related to traditional knowledge
and EA under the MVEIRB (e.g., access to information
versus confidentiality), the importance of providing tradi-
tional knowledge in context (and opportunities for holders
of this knowledge to advise the board on the accuracy and
completeness of any information presented), and potential
methods to communicate traditional knowledge to the
Board members as part of the assessment process.
Ideal Role Taking
Although the literature advocates authority based on sound
argumentation, deliberative democracy also advocates
considering a variety of perspectives. To this end, this
principle considers the degree to which participants are
receptive to different points of view. From a methodolog-
ical perspective, as discussed above, this issue was
conceptualized through the notion of learning. One par-
ticipant explained this context-learning-EA nexus through
the following analogy:
‘‘You have got some serious symptoms and there is
nothing obvious there, but you go to one doctor and you get
one opinion there, if you go to 15 of them you get 15
different opinions, but by going to that number of people,
you are likely to build a very competent case on what is
actually wrong with you. And I think that EA is like that. It
provides scrutiny by more eyes, by eyes from different
sources, because people look at projects in different ways,
both on an individual level, an organizational level, and a
cultural level’’ (Interview 2).
Environmental Management (2008) 42:1–18 13
123
Participants were asked to discuss what they learned
through their involvement, and how this learning was
facilitated through the EA process.
Learning
All participants noted that EIA is a learning process, as
reflected well by the following quotes: ‘‘I think that it is
always a learning experience. And when you have been
around as long as I have, you sometimes think you have
heard it all before, and it’s not true, there is always some
new point to be made’’ (Interview 12) and ‘‘I would find it
inconceivable that EIA isn’t a venue for learning. And if
you haven’t learned, you haven’t done an EIA’’ (Interview
2).
Likewise, all participants identified learning outcomes
associated with participation in the Snap Lake EA.
Learning outcomes addressed a number of aspects that
illustrate both the roles of experience and interaction.
Learning outcomes associated with the EA addressed:
• Project components and impacts (Interview 5, 7, 14,
31)—’’So people are now familiar with acid rock
drainage, they are familiar with dust deposition, they
are familiar with waste rock piles’’ (Interview 31),
• EA process (Interviews 1, 3, 4, 5, 6, 7, 14)—’’We
learned that the information requests rounds, although
beneficial, took a long time, and you didn’t really get
the answer you wanted in a quick time turn around’’
(Interview 1),
• Ways of knowing (Interview 13, 14)—’’Because I do
believe that one of the biggest benefits of living up here
is listening to the elders, because one thing I
learned…is that the elder’s have their own message’’
(Interview 13),
• The community and methods of community engage-
ment (Interview 2, 5, 7 MVEIRB 2005)—’’We learned
a lot about the communities…so building trust and
maintaining it, and maintaining credibility is critical’’
(Interview 2),
• Community capacity—Our organization is now ‘‘say-
ing we don’t want to be another intervenor at the end of
the pipe, we want to involved from the beginning on
monitoring and baseline data collection and not on your
terms—but on [our] terms. So people have really
learned that this is possible. [We] have the capacity to
do that’’ (Interview 14),
• Organizational skills (Interviews 1, 5, 6, 7), including
how to use the process to further organizational
objectives (Interviews 3, 4, 8, 13)—’’The other part
of our strategy is to then make the consistent bank of
messages…[our presentations are] modified for the
specifics, but the general direction, the intent,
objectives, are consistent… So when we go to hearings
now, a number of our starting slides are always the
same, to get across the message—’Here is what we are
after,’ in terms of the general sense of our goals, as [an
organization]’’ (Interview 13),
• Interaction among different organizations (Interviews
12, 13)—’’Of course part of participating in these type
of things is you spend most of the time listening rather
than speaking, and that’s an opportunity to gauge other
peoples’ perspectives on these things’’ (Interview 12),
• How to communicate more effectively (Interviews 2, 3,
4, 7, 12, 13)—’’…the next time it comes around you
can get the visual things out there, and it will have a big
impact, and you don’t have to spend a lot of time
writing out huge reports that people aren’t going to
read, right? Get the things out there that will have an
impact, and aren’t necessarily easy to do, but in the
long term have a much better impact’’ (Interview 4),
and
• Deficiencies in policy regime (Interviews 3, 4, 8, 13).
This last group of learning outcomes indicates recognition
among participants of the fragmented resource manage-
ment system perpetuated by the MVRMA, despite the
intent of the Act to provide a system for resource
management in the North. Although the legislation
strengthens the intersection of EIA and regulatory man-
agement, it perpetuates the project- specific focus of EIA.
Thus, although the public may be actively involved in
project-specific activities, there is no venue for discussing
broader resource management issues that affect these
project-specific activities. As expressed by three partici-
pants, the EA of the Snap Lake project illustrated that no
opportunities arose to consider questions such as: ‘‘Is it
appropriate to pursue economic development directed at
putting a diamond on somebody’s finger?’’ (Interview 31)
and ‘‘Is the current pattern of diamond development
sustainable?’’ (Interviews 3, 4).
Problem fragmentation is seen by the public to be arti-
ficial, and, as such, serves as a regulatory barrier to
deliberative participation in assessment (Petts 2003).
When asked to identify the EA activities most clearly
associated with learning, respondents mentioned activities
that encouraged interaction among participants. Research
participants identified two activities that were cited as
particularly useful: (i) technical sessions—’’I think the
technical sessions, even with all their limitations, that is
where you get into the details. You ask questions, you put
on the table the ‘what ifs’’’ (Interview 7) and hearings—’’I
guess the ones that are most useful to people in general are
the public hearings’’ (Interview 31).
This finding supports previous research that identifies
face-to-face exchange as an important component of
14 Environmental Management (2008) 42:1–18
123
deliberative democracy (Innes 1998; Webler, Kastenholz,
and Renn 1995).
Discussion and Conclusion
The EA process, as exemplified in the Snap Lake project,
addresses, to varying degrees, each of Wilkund’s (2005)
four principles of deliberative democracy. In terms of
generality, the EA was open to all interested parties; and,
although the number of intervenors and directly affected
parties was significantly fewer than those in previous dia-
mond-based EAs, many ‘‘alumni’’ organizations were
copied on all documentation. More research, however, is
needed to determine why some organizations chose not to
participate in the Snap Lake EA, and if their interests were
represented through the assessment process (Davies and
Blackstock 2005). Furthermore, additional attention must
be given to understanding how well the MVRMA serves
individual participants. As noted in the methodology, par-
ticipation in the EA was undertaken through representative
organizations. While the literature (Davies and Blackstock
2005; Parkinson 2003) suggests that this is an appropriate
way to balance deliberation with economy of participation,
we did not test this assertion, but this case indicates that the
MVRMA may provide an appropriate venue for such
testing. Research could also focus on achieving a greater
understanding of the nonparticipant (Diduck and Sinclair
2002) and the relationship between an organization and its
members (i.e., how well members’ views are being repre-
sented in an EA case). Furthermore, research should
consider if representative organizations do indeed promote
active citizenship: do the organizations create a venue
outside the government process to encourage participation
by members, or do they replace involvement by
individuals?
In terms of autonomy, the public was afforded multiple
and varied opportunities to be involved in the EA. Partic-
ipation addressed four of the five ‘‘key’’ provisions for
public participation in EA (Sinclair and Diduck 2005):
notice, public comment, access to information, and hear-
ings. Although the review of the draft terms of reference
and workplan did not take the format desired by some
participants, revisions of the terms reflected a majority of
concerns expressed by participants. What could have been
a significant barrier to active participation appears, in this
case, to have been avoided. This may have been a function
of the EA being the third assessment of a diamond devel-
opment in ten years, and thus the key issues for scoping
were largely known. More likely, however is that the Board
accepted the vast majority of recommended scoping
amendments submitted through written communication,
thus demonstrating that participation had a direct impact.
Perhaps most important to the deliberative potential of
EA revealed in this case was the presence of technical
sessions, which bring interested parties together for a
focused discussion of an issue. Feedback provided during
the assessment, through interviews, and during the post hoc
analysis, focused on the opportunity to sit across a table,
debate, and, where possible, resolve issues as a procedural
strength. Furthermore, hearings, a more traditional means
of facilitating discussion, are more efficient when under-
taken in combination with technical sessions. Successful
technical sessions, however, are facilitated by outside
parties, have a clear purpose, are well scoped, involve a
range of interested parties, and include a clear way to track
the resolution of issues. Additional methods, including
interest-based negotiations and mediation, may also fulfill
this function, although these methods must be tested within
the political and cultural climate of Northern Canada.
Results, however, suggest that rather than include technical
sessions as an addendum to the process, this aspect should
be used in future EA to increase the deliberative potential
of EA under the MVRMA.
Administrative barriers became more pronounced sur-
rounding efforts to neutralize power. Participant funding
(the fifth key provision of public participation) is not
available for EAs conducted under the MVRMA. As noted
in other research (Lynn and Wathern 1991; Sinclair and
Diduck 2005; Webler, Kastenholz, and Renn 1995), access
to financial resources is a key component for facilitating
participation, and while steps were taken to remedy power
imbalances, legislative change is required to provide par-
ticipant funding for future assessments. As a result,
participants had to rely on government, past research, and
other sources of funding to present alternative perspectives.
Although steps were taken to address the cross-cultural
context of the EA, more changes are needed to engage
Aboriginal people in EA, and develop a process that can
more adequately overcome cultural barriers to political
processes (see also Ellis 2005).
Participants had access to and were receptive regarding
different perspectives, as illustrated by learning outcomes
associated with this EA. There is some indication that
participants were able to adopt attitudes of reciprocity and
impartiality, as these are necessary for the types of learning
outcomes identified above, particularly those related to
ways of knowing, community engagement, and interaction
among organizations. An important addendum to this
finding is that interactive processes were identified as being
more conducive to learning (and, by extension, interaction
with other EA participants). This finding supports the view
that learning has a social and contextual dimension (Jarvis
1987; Merriam and Caffarella 1999).
Findings affirmed Wiklund’s (2005) hypothesis that
practice or implementation improves deliberative potential
Environmental Management (2008) 42:1–18 15
123
provided in legislative requirements. While the deliberative
spirit is expressed through the preamble of the MVRMA,
the deliberative potential of the process was actualized in
this case through specific assessment steps. These steps are
more clearly directed through guidelines issued under the
Act, and through EA practice. As noted above, this com-
mitment to involving the public in the decisions that affect
them is considered a strength of the MVRMA (SENES
Consultants Limited 2006). However, because much of the
deliberative potential is situated outside the legislative
framework, it could be lost if the culture of the Board
changes. For example, much of the deliberative potential
expressed through this case was found in technical ses-
sions, a rarely used technique used in the assessment
process, directed by guideline under the Act. The technical
sessions provided an opportunity to resolve complex
technical issues prior to hearings in a dialogical setting, and
participants expressed clear support during this stage of the
EA.
Thus we conclude that EA conducted under the
MVRMA can serve as a deliberative process, as illustrated
by opportunities for dialogue, access to different perspec-
tives, and the learning outcomes associated with
participation in the EA of the Snap Lake project. The
process does encourage interaction and active citizenship,
as shown by the findings and confirmed by spokespersons
for participant organizations. As noted, however, much of
the deliberative potential depends on what the Board
chooses to do in a particular case to involve the public
rather than what is required by the Act. As well, the
absence of participant funding also limits the deliberative
potential of the MVRMA through constraining the infor-
mation that is presented and who can participate. Absent
from this review is an analysis of whether a deliberative
process ultimately leads to better policy decisions. Future
research, as noted by us and others, should endeavor to
address this broader question and thereby more clearly
verify the deliberative potential of EA.
Finally, results illustrate how deliberative democracy
provides a useful lens for evaluating EIA processes
because of its focus on the participatory aspects of policy
development (Parkins and Mitchell 2005; Petts 2003). As
summarized by Baber (2004), the structures encouraged
by deliberative democracy provide ‘‘a concise and general
summary of the requirements cited in EIA research for
impact assessment to achieve its analytical potential
without stunting democratic participation.’’ Beierle
(1999), suggests that a deliberative analysis addresses a
range of aspects, including representation, process,
information, and outcomes. Wiklund’s (2005) framework
is able to capture each of these aspects, particularly when
consideration is given to learning associated with
participation.
Acknowledgments The authors wish to thank research participants,
who volunteered to participate and provided wise insight about the
MVRMA and the Snap Lake EA. We would like to acknowledge the
two reviewers whose questions and comments greatly strengthened
the document. Financial support for this study was provided by the
Social Sciences and Humanities Research Council of Canada, and the
Northern Studies Research Training Program.
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