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    The Environmental Petitions Process:

    Enhancing environmental governance through

    transparency, public participation and accountability

    Liohn Sherer

    Office of the Auditor General,

    Commissioner of the Environment and Sustainable Development

    September 23, 2011

    Word Count: 13,000

    Abstract: Measuring the effectiveness of sustainable development policies and programs

    is a challenge for governments worldwide. The aim of this paper is to contribute to the

    measurement of Canadian efforts to achieve sustainable development by evaluating the

    Environmental Petitions Process (EPP). The EPP allows Canadian citizens to submitquestions and requests regarding the environment and sustainable development to the

    Federal Government. The evaluation is based on three pillars of effective environmentalgovernance: transparency, public participation, and accountability. Definitions of theconcepts are developed with reference to the environmental governance literature, and

    their complex interrelationships are explored. The EPP contributes to transparency by

    providing the public with a mechanism to access a wide variety of information aboutdecision-making rationales, processes and impacts. The public can use the Process to

    directly influence decisions and to feed information into the decision-making systems of

    both Government and Parliament. Finally, the Process gives both Parliamentarians and

    citizens the information they need to hold the Government accountable, and gives citizensa mechanism for doing so by requiring Ministers to respond to the publics questions.

    Despite the effective design and strong potential, the Process effectiveness is dependent

    on the participation of the public. Few petitions are received (the number peaked at 47 in2008) and participation is declining (only 19 were received in 2010). As such, the valueof the Process outputs is questionable at best. Further research is recommended to

    measure the extent of its contribution to sustainable development in Canada.

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    Contents

    1. INTRODUCTION ................................................................................................................ 1

    2. BACKGROUND ................................................................................................................... 2

    3. THREE PILLARS OF ENVIRONMENTAL GOVERNANCE ....................................... 6

    3.1. TRANSPARENCY ............................................................................................................. 7

    3.2. PUBLIC PARTICIPATION ................................................................................................... 93.3. ACCOUNTABILITY ........................................................................................................ 10

    4. EVALUATING THE ENVIRONMENTAL PETITIONS PROCESS ............................ 13

    4.1. TRANSPARENCY ........................................................................................................... 134.2. PUBLIC PARTICIPATION ................................................................................................. 16

    4.3. ACCOUNTABILITY ........................................................................................................ 19

    5. CONCLUSIONS ................................................................................................................. 22

    6. RECOMMENDATIONS FOR FURTHER RESEARCH ............................................... 24

    A. DESCRIPTION OF INTERNSHIP ................................................................................ A-1

    B. HOUSING DEVELOPMENT NEAR MISSION, BRITISH COLUMBIA ................. A-3

    C. FOLLOW-UP PETITION ON A HOUSING DEVELOPMENT NEAR MISSION,

    BRITISH COLUMBIA ............................................................................................................. A-8

    D. FOLLOW-UP PETITION ON A HOUSING DEVELOPMENT NEAR MISSION,

    BRITISH COLUMBIA ........................................................................................................... A-12

    E. FOLLOW-UP PETITION ON THE SILVERMERE HOUSING DEVELOPMENT IN

    MISSION, BRITISH COLUMBIA ........................................................................................ A-18

    F. FOLLOW-UP PETITION ON A HOUSING DEVELOPMENT NEAR MISSION,BRITISH COLUMBIA ........................................................................................................... A-26

    G. BIBLIOGRAPHY ........................................................................................................... A-31

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    1. IntroductionIncreased study in recent years of the policies needed to move towards sustainabledevelopment has shed new light on the shortcomings of national and international

    attempts to achieve it. These shortcomings include unaccountability of officials, lack of

    transparency, limited opportunities for participation and dissatisfaction with performance(Markell, 2006, p. 653). The result has been a growing emphasis on governance as a

    critical underpinning of policy success generally and environmental progress more

    specifically (Esty et al., 2005, p. 28). The concept of governance has come to refer tothe totality of mechanisms and instruments available for influencing social change in

    preordained directions (Lafferty, 2004, p. 5). Once the available mechanisms and

    instruments are identified and implemented, the challenge becomes how to measure theirprogress and effectiveness. The aim of this paper is to contribute to the measurement of

    the success of Canadas efforts to achieve sustainable development by evaluating one of

    Canadas mechanisms for doing so, the Environmental Petitions Process (EPP).

    In their 1993 campaign platform, the Liberal party of Canada promised to strive to meet

    the vision of the 1987 Brundtland report (Liberal Party, 1993, p. 64).

    The proposedmeasures included a mechanism that would allow individuals to submit petitions

    requesting action when environmental policies or laws were being ignored or violated. In

    1995, amendments to the Auditor General Act laid out the guidelines for theEnvironmental Petitions Process, establishing the Commissioner of the Environment and

    Sustainable Development (CESD), responsible for providing sustainable development

    monitoring and reporting, and the Environmental Petitions Process as one of his tools

    (Canada, 2010). Through the EPP, citizens can direct questions or requests for action tofederal departments and agencies with environmental portfolios, and these departments

    and agencies are obligated to respond.

    One response to the question of how to achieve sustainable development has been

    recognition at the international level of three prerequisites for effective environmentalgovernance. Principle 10 of the Rio Declaration on Environment and Development set

    out three requirements for effectively addressing environmental issues: Access to

    information, the opportunity to participate, and access to redress and remedy (UN, 1992).The Aarhus Convention, the primary affirmation of which is to protect the state of the

    environment and ensure sustainable development (UNECE, 1998, p. 2), emphasizes

    transparency, public participation, and accountability (Stec & Casey-Lefkowitz, 2000, p.

    1 par. 3). The objective of this report is to develop clear definitions of the three pillars transparency, public participation, and accountabilityand to evaluate how the EPP can

    contribute to sustainable development in Canada by enhancing them. In doing so, this

    report will identify measurable outcomes of the Process, which can be used in the future

    to assess its progress and effectiveness.

    Canada is not immune to the indictments of democratic institutions mentioned above. It

    has been accused of having a deeply entrenched culture of secrecy and of favouring

    bureaucratic control over public participation (AIRTF, 2002; Warriner, 1997, p. 176). The

    EPP, despite its potential to address such accusations, has faded into obscurity in theyears since its creation. Though the CESD submits annual status reports on the Process, it

    has never been the subject of independent review, and no significant changes have been

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    made since its original implementation. It has gone essentially unnoticed by the academic

    and professional communities, and reviews of the environmental and governance

    literature return only a few brief and fleeting mentions of the CESD and the EPP. TheEPPs absence from the critical study of environmental governance in Canada is a

    significant omission, one that must be remedied if the Process is to remain relevant and

    effective, and if Canada is to continue to progress towards sustainable development.This paper begins by providing a background and overview of the EPP and the CESD inSection 2. Section 3 develops the lens through which the EPP is evaluated in Section 4.

    Finally, Section 5 offers conclusions and recommendations for further research and

    analysis.

    2. BackgroundWith the 1987 publication of the Brundtland Report Our Common Future, sustainable

    development was launched onto the world stage (World Commission on Environment and

    Sustainable Development, 1987). At the same time that the Brundtland Commission waspublishing its report, CanadasNational Task Force on the Environment and the Economy

    was publishing a report calling on Canadian government, industry, academics and NGOsto develop information-generation systems, public involvement processes and formalmechanisms for holding Ministers and departments accountable for environmentally-

    sound development (National Task Force on the Environment and the Economy, 1987,

    pp. 5, 8). These recommendations were eventually adopted by the Government inamendments to theAuditor General Actin 1995.

    The primary products of the Office of the Auditor General of Canada (OAG) are audits:

    performance, annual, and special examinations (OAG, 2004, p. 89).1

    The OAG defines a

    performance audit as a systematic examination of government activities that provides

    Parliament with information and recommendations designed to promote accountable

    government, good governance, and sustainable development (OAG, 2004, p. 13). Anaudits scope includes the examination of economy, efficiency, cost effectiveness and

    environmental effects of government activities. Audit reports are made public ensuringthat citizens have access to the information and the recommendations provided to

    Parliament.

    The 1995 amendments established the Commissioner of the Environment and Sustainable

    Development (CESD) in the OAG, and within his mandate the Environmental PetitionsProcess (EPP). The goal was to increase government legitimacy and support a turn

    towards sustainable development by enhancing transparency, public participation, and

    accountability. The CESD is one of the first such offices in the world, and has beenreferred to as Canadas comparative advantage in the early twenty-first-century

    experiments with institutional change (Toner & Frey, 2004, pp. 214-215).

    1The Office of the Auditor General of Canada has one business line legislative auditingand six

    product lines: annual audit of the summary financial statements of the Government of Canada; annual

    audits of Crown corporations and other entities (federal, territorial, and international); special examinations

    of Crown corporations; performance audits of departments and agencies; environment and sustainable

    development monitoring activities; and assessments of agency performance reports. (OAG, 2004, p. 9)

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    Canadas Access to Information Act (ATIA) was enacted in 1983, more than 10 years

    before the EPP, ostensibly to enhance government transparency. Freedom of information

    laws are a common response to transparency needs, and as of 2006 had beenimplemented in nearly 70 countries worldwide (more than half of those in the preceding

    decade) (Banisar, 2006, p. 6). Two significant distinctions explain why the petitions

    process was established despite, or to complement, ATIA. First, ATIA makes accessibleonly documented information such as letters, memos, e-mails, photographs and maps. Asopposed to countries such as New Zealand and Denmark, unrecorded information

    telephone calls, oral conversations, or the contents of meetings is not covered. Second,

    to be truly transparent, decisions must include all the potentially relevant information thatwas taken into account in making them, in such a way that others are able to reconstruct

    the decision processes and intended outcomes (Drew & Nyerges, 2004, p. 34). If such

    information exists, then ATIA ensures its accessibility. Unfortunately, such information is

    difficult to compile, time consuming to maintain, and is unlikely to exist for the majorityof government decisions. The EPP fills these gaps, as will be seen in section 4.1.

    The position of Commissioner of the Environment and Sustainable Development was

    created in 1995 following the recommendations of the First Report of The StandingCommittee on Environment and Sustainable Development (1994). In response to thisreport, the government made commitments to openness, transparency and leadership in

    the pursuit of sustainable development (Minister of the Environment, 1994, p. 4). The

    Commissioner is responsible for a range of activities related to providing parliament withinformation, analysis and recommendations on the governments efforts to protect the

    environment and move towards sustainable development (CESD, 2008). These activities

    include auditing the environmental performance of federal departments, agencies, and

    crown corporations; assessing the federal governments sustainable development strategyand whether federal departments are meeting their sustainable development objectives;

    managing the environmental petitions process; and reporting on Canadas progress

    towards meeting its obligations under the Kyoto Protocol.

    The environmental petitions process is intended to be a way for Canadians to bring theirconcerns about environmental issues to the attention of the federal government (CESD,

    2008, p. 5).It is managed by the Commissioner of the Environment and Sustainable

    Development, who reports annually to Parliament on the number, nature, and status ofpetitions, and on departmental compliance with the statutory requirements. Petitions may

    also become the subject of audits undertaken either by the CESD or other teams in the

    Office of the Auditor General.

    Environmental petitions are unlike other public petitions in that they do not need to havea minimum number of signatures, nor do they need to demand action. In fact, petitions

    are essentially no more than a letter addressed to the CESD. They can be sent by anindividual or a group and can request a wide variety of responses, including:

    Investigations into alleged violations of federal laws or regulations; Action on matters of federal environmental management; Explanations of federal policy or involvement in particular issues; Reviews and improvements of federal laws; Responses to comments or suggestions;

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    Explanations of actions in response to public commitments; Information on efforts to reduce environmental impacts of operations; or Outlines of how international commitments are being met (CESD, 2008, p. 7).

    The Commissioner does not respond to petitions or validate, investigate, or substantiatethe responses from Ministers. In managing the process, the Commissioner reviews

    petitions to ensure they are eligible, determines the relevant Ministers and forwards thepetitions, and monitors the status of responses. Petitioners can identify explicitly the

    Ministers to which they would like their questions forwarded, but can also leave the letter

    open-ended and allow the CESD to forward questions to any and all relevant Ministries.

    The requirements for a petition to be considered admissible are minimal:

    They must be received in writing; They must be sent from a resident of Canada; and They must relate to an environmental matter in the context of sustainable

    development under the responsibility of a category I department.

    2

    Ministers are required to acknowledge receipt of the petition within 15 days and provide

    a response within 120 days.

    Once a year, the Commissioner provides Parliament with a summary of the petitionsreceived and tables the petitions. The Commissioner also maintains an online registry of

    all petitions and responses received.3

    Since the process was established in 1996, more

    than 350 petitions have been received (see Figure 2).

    The CESD can, and does, use petitions to inform the choice of entities to audit, case

    studies to examine, and criteria to assess. For instance, between 2007 and 2010 theCommissioner received twenty petitions associated with the use of science in decision-

    making,4

    resulting in an audit of science-informed decision making to supportenvironmental management planned for late 2011. In many cases, responses to petitionsaddress the questions raised and satisfy the petitioners expectations (CESD, 2007, p. 78).

    In some cases, however, the issues raised warrant further investigation, and in these cases

    the CESD has the tools and powers necessary to delve deeper, seek answers, and makethe results public.

    Because petitions are often submitted not by experts but by average citizens concerned

    with a local issue, clarityof context, information, and requestswas a significant issue

    for many years. Unclear questions prevented ministers from responding in ways thatsatisfied petitioners. To address this issue, the CESD published a guide to writing

    petitions in 2008, which included advice, suggestions, and a standard template to follow.

    In that guide, the CESD also recognized that petitioners may find it difficult to identifythe departments or agencies responsible for the issue in question. In those cases, the

    2 There are 28 category I departments as defined in Section 2 of theAct. A list of federal departments and

    agencies subject to the environmental petitions process can be found in (CESD, 2008, p. 6).3 The petitions Catalogue can be accessed at http://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.html4 Petitions no. 100b, 192, 194, 200, 203, 215, 220, 221e, 224, 238, 259, 262, 283, 290, 291, 292, 294, 297,

    298, and 300. The petitions catalog can be found athttp://www.oag-

    bvg.gc.ca/internet/English/pet_fs_e_929.html

    http://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.html
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    CESD advised that petitioners use wording that would allow the Commissioner to

    forward the petition to additional departments or agencies. Petitioners are also advised to

    anticipate likely responses from ministers and to include follow-up questions, to avoidthe necessity of submitting follow-up petitions and extending even more the timeframe

    for receiving the responses they want. The guide discourages petitioners from phrasing

    questions in a manner that can be answered with a simple yes or no, as those types ofresponses are both easier for the ministers to offer and unlikely to satisfy the petitioner.Other outreach attempts to raise awareness of the EPP have included a video posted on

    YouTube.5

    To better demonstrate the characteristics of a petition and responses, consider the

    following example. The petitions and responses are included in the Appendix. In 2003,the Genstar Development Company proposed to develop 100 single family residences on

    Silvermere Island, B.C., and the adjacent peninsula (Bertelsen, 2003). The island was part

    of an ecosystem that hosted an annual salmon run and spawning ground and was home to

    a number of endangered species and species at risk. In July 2004, an area residentsubmitted a petition claiming that the proposed development would cause significant

    damage to the ecosystem. The majority of the petitions two pages consisted ofbackground information. It included no specific questions, but rather the statement thatthe petitioner believed a statutory review/Canadian Environment Assessment Actreview

    is required before any further environmental damage is done (Lyster, Housing

    development near Mission, British Columbia: No. 122A, 2004). The joint response fromthe Minister of the Environment and the Minister of Fisheries and Oceans did not address

    the majority of the petitioners concerns (environmental degradation, loss of biodiversity,

    threats to fish habitat), but focused instead on the statutory requirements for

    environmental assessments and how, in the case, none of those requirements had beentriggered (Dion, 2004). In the ensuing years, the petitioner has submitted four follow-up

    petitions.

    The second petition was one page long, and similarly did not contain explicit questions.

    The Department of Fisheries and Oceans (DFO) response to the second petition,submitted in January 2005, noted that DFO had in fact objected to a proposal by the

    proponent to conduct a large scale drawdown of the Silvermere Lake:

    With respect to the large scale drawdown, it was DFOs assessment that theEnvironmental Management Plan did not provide sufficient information to ensure aclear understanding of the extent of the works and potential impacts to fisheriesresources in Silvermere Lake, and the Stave River watershed. The proponent wasrequested to submit further detail regarding project design and mitigation. (Regan,

    2005)

    The response also noted that while no requirement for a federal EIA had been triggered,the Department would complete the appropriate reviews if and when they became

    necessary.

    The third petition was submitted in February 2006, again without explicit questions andfocusing on the necessity of an EIA, to which the Ministers responded that the proponent

    5http://www.youtube.com/watch?v=rqqo4AO4WZE

    http://www.youtube.com/watch?v=rqqo4AO4WZEhttp://www.youtube.com/watch?v=rqqo4AO4WZEhttp://www.youtube.com/watch?v=rqqo4AO4WZEhttp://www.youtube.com/watch?v=rqqo4AO4WZE
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    was in the process of preparing an environmental assessment (Lyster, Ambrose, Hearn, &

    Cannon, 2006).

    The fourth and fifth petitions were submitted in March 2007 and August 2010,

    respectively. Each contained explicit questions directed at specific Ministries, addressinga variety of concerns including EIAs, wildlife impacts, and environmental degradation.

    The response to the fourth petition was detailed and addressed each question individually.At the time of writing, the response to the fifth petition had not yet been published to theonline catalogue.

    This example parallels the evolution of the petitions process. Between 2003 and 2010,

    petitions progressed from short letters expressing concern with an activity to include

    detailed background information, clear statements of concern, and explicit questionsrequesting detailed responses and actions. However, it also shows the frustration that can

    be experienced by petitioners. Six years later, the petitioners questions and concerns

    have still not been satisfied, the proponent continues to develop the proposal, and the

    alleged environmental degradation persists.

    The 2005 study Benchmarking National Environmental Stewardship used anenvironmental sustainability index based on 21 indicators. Of the 21 indicators,

    environmental governance correlated most strongly to the 76 underlying variables,

    suggesting that countries that pay the most attention to environmental policy are morelikely to produce successful environmental outcomes. The study ranked Canada 24

    thout

    of 146 in environmental governance, and made no mention of the Environmental

    Petitions Process (Esty et al., 2005, p. 371).

    One reason the process goes unnoticed by the international community may be that thereare no other mechanisms to which it can be directly compared. The United States has no

    environmental commissioner or ombudsman and no formal process for the public to

    provide input into or request information about environmental matters. Nor are

    comparable petitions processes or environmental ombudsmen identified in Scandinavia,often seen as a bastion of environmental progress. The response from a Swedish contact

    is telling, noting that the closest comparison to the EPP in that country is a well-

    entrenched culture of transparency and strong access to information legislation. Petitionscommittees exist in many Parliamentary democracies, though none that are dedicated

    solely to environmental matters or are as well defined as the Canadian example.

    Environmental commissioners exist in Ontario and New Zealand, but there are significant

    differences with these institutions as well. Many of these comparable, though different,mechanisms will be presented in the following sections as examples, or to provide a

    contrast or frame of reference for the EPP.

    3. Three Pillars of Environmental GovernanceThis section provides the lens through which the EPP will be evaluated in Section 4. It

    does so by defining the concepts of transparency, accountability, and public participation

    in reference to the environmental governance literature, as well as other literatures relatedto sustainable development and environmental policy. The concepts consistently reappear

    across the literature in different forms and different contexts, but almost always in

    relation to each other. Baumert and Petkova, for instance, interpret the term public

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    participation as referring to a set of core principles that, broadly speaking, promote

    transparency, public engagement, and accountability (2000, p. 2). Voisey and ORiordan

    identify the same three ideas as requirements for institutional movement towardssustainable development (1997, p. 48). Their relationship is summed up best by Hood:

    Transparency in the sense of general disclosure of information about the affairs of

    government provides necessary raw material for democratic accountability because it enables concerned citizens and interest groups to be sufficiently informedabout the activities of executive government to be able to feed their views effectivelyinto the legislature or other forums. (2010, p. 992)

    Due to the sheer extent of the literature exploring these three concepts, the work reviewedfor and presented in this paper is by necessity not exhaustive. Rather, the goal is to define

    the terms in relation to effective environmental governance, and to explore them in a way

    that makes their interdependencies and interrelationships are clear.

    3.1.TransparencyTransparency has been referred to as the buzzword solution to the gamut of governance

    issues together known as the democracy deficit (Hale, 2008, p. 73). It has been creditedwith a catalogue of benefits, including enhancing the equity, effectiveness, and efficiency

    of participation; narrowing the gap between the public and decision-makers; leading to

    more informed decisions; empowering the weak; and holding decision-makersaccountable (Drew & Nyerges, 2004, p. 35; Gupta, 2010, p. 1). Carolyn Ball has traced

    its evolution from an etymological perspective, concluding that the term has many

    meanings, but overall is about open decision-making and the ease of access and use of

    government and nonprofit information (2009, p. 303).

    While a significant body of literature has been developed around the concept of

    transparency, no single, formal definition of the term is offered in relation to

    environmental governance (Drew & Nyerges, 2004, p. 36). Principle 10 of the RioDeclaration reads that each individual shall have appropriate access to informationconcerning the environment that is held by public authorities but does not define of what

    such information consists nor how it should be made accessible (UN, 1992). The Aarhus

    Convention, despite providing detailed definitions of Environmental Information andhow and under what circumstances it shall be made accessible, as well as making many

    explicit references to the desirability of transparency, does not define the term itself

    (UNECE, 1998). At its most fundamental level, though, transparency is about the

    normative right to know (Gupta, 2010, p. 4).

    Drew and Nyerges (2004) identify a range of concepts often discussed in association with

    transparency, from which they isolate seven objectives including accessibility,

    accountability, and openness. 6 A more useful context in which to place transparency forthe purposes of this paper is offered by the first pillar of the Aarhus Convention, Accessto Information. In this context, two forms of access to information are defined: Passive,

    where public authorities provide information in response to requests; and Active, where

    6 The seven objectives for transparency are: Integration into broader decision context; Accessibility; Logic

    and rationale; Accountability; Truth and accuracy; Openness; Stakeholder involvement; and Clarity (Drew

    & Nyerges, 2004, p. 36)

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    3.2.Public ParticipationDespite the grand hopes for transparency, information does not in and of itself guarantee

    a shift towards sustainable development. While information can empower individuals to

    exert influence on decision-makers (Dingwerth & Eichinger, 2010, p. 74), disclosurepolicies can be designed in ways that sidestep real, meaningful citizen empowerment

    (Florini, 2008).This, it has been argued, is the case with Canadas Access to InformationAct(Worthy, 2010, p. 567). To truly enhance environmental governance, the informationmade available by sunshine laws must be wielded by the public to affect change (Fuentes,

    2008, p. 2; Flscher, 2007, p. 100).

    Public participation has been highlighted as another strategy for achieving many of the

    same goals as transparency, including increasing government legitimacy andaccountability, strengthening democratic principles, and enhancing equity (Markell, 2006,

    p. 653; Warriner, 1997, pp. 176, 181). This second pillar operationalizes the first:

    information gained through improved transparency leads to changes in the actions of

    policy-makers when it is used by the public to bring about those changes (Weil et al.,2006, p. 156). At the same time, this second pillar relies on the first: true participation is

    possible only when the public has information about the government, its policies and its

    decision-making practices (Stec & Casey-Lefkowitz, 2000, p. 6) (Banisar D. , 2006, p. 6).

    Alone, neither is sufficient, but in conjunction with transparency, public participationoffers the substantive improvements in environmental performance identified by Gupta

    to inform, empower, and improve (2010, p. 4).

    Significant study of participation is conducted at the project-specific level within

    environmental impact assessment, which faces recurrent criticism for outcomes that areunfair, unjust, and inequitable (Lawrence, 2005). The insights revealed by this literature

    have broader implications for the more ongoing, process-level concerns in public policy

    and governance (O'Faircheallaigh, 2010). Regardless of the discipline, the work falls into

    two distinct categories: distributive justice, which is concerned with the fairness of theoutcomes of decisions; and procedural justice, which is concerned with the fairness of the

    decision-making process (Illsley, 2003).

    Broadly defined, public participation is about how people communicate their views topolicymakers in a purposeful and organized manner, and can refer to anything from

    voting in general elections to public demonstrations (Warriner, 1997, p. 173). In the

    context of environmental governance, however, it is more useful to conceive of public

    participation as structured mechanisms whereby citizens influence decisions about plans,policies and programs.

    Depending on the body of literature, the core differentiating components of participation

    can include the degrees of participation (as in Arnsteins hierarchical ladder), thedirection of communication flows, or the objectives for which participation is used (Reed,2008). The environmental governance community has often cited Langtons typology of

    participation (1978, p. 21), which divides participation mechanisms into four classes

    based on the nature of the roles played by the citizens: (1) Obligatory participation; (2)

    Electoral participation; (3) Citizen involvement; and (4) Citizen action (Warriner, 1997).In this paper I examine a group of mechanisms that falls between Langtons third and

    fourth levels: processes that are controlled and managed by government, but initiated by

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    individuals or groups of citizens. The major purpose of the former is to improve decision-

    making, and of the latter to influence decisions (Langton, 1978).

    The degree to which an environmental governance mechanism encourages or enhances

    participation is dependent on many factors. One such factor is a central point of contactfor citizens. Germany, Scotland, the CEC, New Zealand, Ontario and the EU each have a

    central point of contact, which is responsible to varying degrees for receivingpetitions and complaints from citizens, forwarding them to appropriate bodies forresponse, and following up where appropriate.

    8These bodies enhance participation by

    simplifying the submission or complaint procedure and making it more accessible. Where

    such bodies do not exist, it becomes more difficult for citizens to participate. In Quebec

    and the United Kingdom, for example, where parliamentary petitions must be submittedthrough members of parliament, potential petitioners must identify members of

    parliament who might be willing to accept and present the petition, and contact the

    members directly (Quebec, 2010; Cavanagh et al., 2000, p. 71).

    Another factor that affects how a process enhances public participation is the definition ofa request. Under Ontarios Environmental Bill of Rights (EBR) for instance, citizens

    can apply for either a policy review or an investigation of an alleged violation (Ontario,

    1993).9

    This allows them to directly influence policy-making and environmental

    management processes, but prevents them from submitting other types of requests. Incontrast, the Scottish Parliament must consider any petition addressed to it (Scottish

    Parliament, 2009).10

    This allows petitioners to request, for example, explanations of how

    a decision was reached (enhancing procedural justice) without precluding the types ofrequests explicitly identified under Ontarios EBR. The trade-off is between efficiency

    and flexibility: A system with an explicit regulatory aim may be more efficient than an

    open system at achieving that specific aim, but an open system may be effective at

    addressing a broader range of governance issues.

    The results of enhanced public participation fall into two categories: improvements indecisions themselves and improvements in the decision-making process. The concept of

    procedural justice suggests that they are equally important, and transparency helps to

    shed light on both. The study of public participation is about how citizens useinformation to engage in the decision-making process and influence decisions and their

    outcomes. Participation mechanisms, together with enhanced transparency, allow the

    public to hold the Government accountable, as will be seen in the next section.

    3.3.AccountabilityJust as with transparency and public participation, accountability has been adopted as thevehicle for a wide range of governance improvements, as described by Abels in her

    exploration of the links between citizen involvement, legitimacy and accountability(2007, p. 106). Again, the relationships between accountability and the other two pillars

    are complex and multidirectional. Transparency itself becomes a tool for holding thepowerful accountable (Dingwerth & Eichinger, 2010, p. 74), and citizen participation

    8 (German Bundestag) Basic Law of the Federal Republic of Germany: Article 45c(1); (Scottish Parliament,

    2009) Rule 6.1.5(g); (CEC, 2000); (New Zealand, 2011); (Ontario, 1993) Article 74.(1); (EC, 2010)9 Articles 61.(1), 74.(1)10 Rule 15.4.1

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    often becomes equated with better accountability (Abels, 2007, p. 103). Accountability

    was identified by Canadas Standing Committee on Environment and Sustainable

    Development as one of the key principles for promoting sustainable development infederal decision-making (Minister of the Environment, 1994, p. 4).

    Bovens has described it as a principle filled with good intentions, loosely defined

    concepts, and vague images of good governance (2006, p. 7). In contrast to the first twoterms, though, the study of accountability is well developed, and a number of formaldefinitions has been offered (Fearon, 1999, p. 55; Przeworski et al., 1999, p. 10; Schedler,

    1999, p. 17). In attempting to provide a definition of government accountability that

    avoids the ambiguity and confusion of defining the term based on its anticipated results,

    Philp offers the following:

    A is accountable with respect to M when some individual, body or institution, Y,can require A to inform and explain/justify his or her conduct with respect to M.

    (Philp, 2009, p. 32)

    What is unique about Philps definition is the absence of explicit sanctions and rewards.

    Across a wide array of accountability mechanisms, the ability to sanction plays a centralrole: from the bottom-up, the public can choose not to re-elect governors who havefailed; from the top-down, Parliaments can defeat governments and governments can

    replace ministers. According to Philp, though the possibility of reward or sanction may be

    desirable for further enhancing accountability, it is not essential to accountabilityper se.

    Philp builds on Bovens exploration of accountability. Bovens argues that thoughsanctions are prerequisites of an accountability relation, the term itself is too narrow and

    exclusionary, and prefers instead the broader expression the actor may face

    consequences (Bovens, 2006, pp. 10-11).

    As opposed to formal sanctions, such

    consequences can be informal or implicit, including requiring decision-makers to explainor justify their conduct.

    The effectiveness of such informal sanctions or consequences may be an extension of the

    importance of procedural justice, the predominance of process over outcome in

    establishing legitimacy. While one might assume that the outcomes of decisions are thecritical factor in influencing perceptions of legitimacy and thus that sanctioning the

    makers of poor decisions is a prerequisite for holding decision-makers accountable this

    is not necessarily the case. In fact, the work on procedural justice calls this assumptioninto question, and asserts that people are just as, if not more, concerned with how

    decisions are made and the fairness of the process (Markell, 2006, pp. 677-678).

    Understanding of the reasons behind decisions can generate support for them and reduce

    dissatisfaction (Banisar D. , 2006, p. 7). As such, holding decision-makers accountableand safeguarding the legitimacy of government decisions may depend more on exposing

    the decision-making processrequiring decision-makers to inform and explain or justify

    their conductthan on punishing or rewarding them for the outcomes of those decisions.

    Abels introduces the term accountability communication, referring to communicationthat includes explanations, justifications, debate and the possibility of questions and

    answers (2007, p. 106).

    Traditionally, government has been subjected to political accountability: Ministers

    answering to Parliament on a retrospective basis to justify the actions they have taken

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    (arrow 5 in figure 3) (Joss, 2010, p. 409). Governments worldwide are increasingly being

    subjected to conceptions of managerial accountability: Downward responsibility to

    clients (citizens), in both retrospective and prospective manners, on a performance basis(arrow 6 in figure 3) (Joss, 2010, p. 409). For instance, as part of Devolution, Scotlands

    petitions system was designed in the late 1990s specifically to make parliament more

    accountable to the people (Carman C. , 2010, p. 735). The citizen submissions process ofthe CEC was created as well to make North American countries more accountable withregards to their environmental laws (Markell, 2006, p. 656).

    The mechanisms researched for this paper petitions, complaints, and compliance

    proceduresall perform the function of requiring governments to inform the public or to

    explain and justify their actions. Where the obligation to respond is strongest, thecontribution to accountability is greatest. In Scotland and Germany, though the Petitions

    Committees must consider all admissible petitions, they are not required to take any

    further action, and where petitions are not pursued, petitioners may be provided only with

    notice that the matter has been closed.11

    In these cases, holding the Government toaccount is at the discretion of the Committee, not the citizen. In Quebec and the United

    Kingdom, where petitions must be submitted to members of parliament, MPs are underno obligation to accept petitions, the result being that there is no guarantee that citizensare able to communicate their concerns to the Minister, department, or body in question

    (Quebec, 2010; Cavanagh et al., 2000, p. 71). In contrast, requests in Ontario must at the

    least be forwarded to the appropriate Ministry or Committee, and citizens are providedwith either the results of subsequent investigations or an explanation of why no further

    investigations were undertaken (Ontario, 1993).12

    The obligation to respond goes hand-in-hand with mandated or suggested timelines.

    Though in most cases the systems I examined guaranteed that the submitter would

    receive a response, the nature and timeliness of the response varied, and as a result thenature of the systems contribution varied.

    While some of the comparable mechanisms offer the possibility of sanctions from the

    European Commissions capacity to litigate to the CESD's power to make

    recommendations to Parliamentnone include explicit powers to sanction. Regardless, itis by no means self-evident that this characteristic impedes their effectiveness at holding

    governments accountable. Government accountability is about more than sanctions. It is

    about responsibility to the people affected by decisions, and in Canada, to the Parliamentthat charges Government with those decisions. As we will see, the mechanisms allow the

    public to make effective use of the information to which they provide access, and in

    doing so contribute to the global governance movement towards sustainabledevelopment.

    This section identified three concepts as pillars of environmental governance, and definedthem in the context of that literature. While transparency, public participation and

    accountability have each been highlighted as the key to effective environmental policies,

    11 (Scottish Parliament, 2009) Rule 15.4 Bringing petitions: "1. The parliament shall consider, in

    accordance with the provisions of the Rule and Rules 15.5 to 15.8, any petition addressed to it. ;

    (German Bundestag) Principles of the Petitions Committee governing the Treatment of Requests and

    Complaints: Article 7.14.712 Articles 7780

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    here I have demonstrated that this is possible for all three only in conjunction with each

    other. Transparency provides the information which the public can use to engage in the

    decision-making process, influence decisions, and hold the Government accountable.Based on this, the next section will evaluate the EPP to determine how it contributes to all

    three pillars.

    4. Evaluating the Environmental Petitions ProcessThis section evaluates the EPP through the lens developed in Section 3, examining how

    each facet of the Process enhances transparency, public participation, and/or

    accountability. I address each pillar in order, first exploring how the EPP contributesdirectly, and then elaborating on how housing the Process within the Office of the Auditor

    General allows the CESD to enhance the process contributions to each pillar by

    integrating petitions into his other roles.

    4.1.TransparencyThe contribution of the petitions process to transparency in Canada is, to some extent,

    self-evident: Fundamentally, the process is about getting information to the public, orrather, allowing the public to get information from the government. The distinctions

    drawn in Section 2 between passive transparency / sunshine laws on the one hand, and

    active transparency / regulatory disclosure on the other, are based on two characteristics:The primary actor, and goal specificity. In the case of the petitions process, neither is

    clear cut.

    Regarding the first characteristic, the primary actor, petitions are submitted by individuals

    and responded to by ministers, suggesting that the process is passive. Petitions anddepartmental responses are subsequently published in the petitions catalogue,

    13a

    proactive disclosure that blurs the line between passive and active. However, inasmuch as

    the petitions catalogue invokes aspects of active disclosure, the Auditor General Actdoesnot go far enough in establishing an active publication role within the petitions process.There is no regulatory definition or specification of information that must be published

    on a routine basis. Rather, it is left to citizens to request information from the

    Government, which plays an exclusively passive role. The information that getspublished through the process is entirely dependent on the activity of citizens. Perhaps a

    better analogy for the line between active and passive is not that it is blurred, but rather

    that it is redrawn to include disclosure in the passive camp.

    Regarding the second characteristic, goal specificity, though there is no specificregulatory aim to the process, its scope is limited to specific environmental and

    sustainable development issues (CESD, 2010). While the regulatory improvements the

    process was designed to achieve are ill-defined if at all, the general goal of the processcan be narrowed down: The environmental petitions process can play a key role inensuring good federal management of environmental and sustainable development

    issues (CESD, 2008, p. 1).To place it in context, the EPP falls somewhere between the

    petitions processes of Germany and Scotland, which are open to any and all matters

    under parliamentary jurisdiction, and the citizen submission process of the CEC, which is

    13 The petitions Catalogue can be accessed athttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.html

    http://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.htmlhttp://www.oag-bvg.gc.ca/internet/English/pet_fs_e_929.html
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    restricted to studying matters that advance the ten objectives set out in the NAAEC

    (NAAEC, 1993).14

    The Scottish Petitions Committee received 960 petitions between 1999 and 2006,

    distributed across 24 subject areas. Of those, just over six percent (61 petitions) related tothe environment (Carman C. J., 2006). In contrast, the CESD received 170 petitions

    between 1999 and 2006, all related to environment and sustainable development. At thesame time, the EPP has avoided the criticisms directed at the citizen submissions processthat the scope of investigations is so severely limited that they no longer address the

    submitters main concerns (Garver, 2008). By addressing a range of goals narrower than

    that ofScotlands petitions committee but broader than that of the CEC, the EPP may be

    able to target issues specifically relating to sustainable development in a broad enoughmanner that it remains relevant and effective.

    The EPP fills two gaps left by ATIA, as discussed in section 2. The first is access to

    information that may not have been recorded: information transmitted in phone calls, oral

    conversations, or meetings. In this case, the two processes complement, rather thancompete with, one another. While Ministers sometimes refer petitioners to recorded

    documentation available throughAccess to Information requests,15 the petitions process is

    intended to provide views and positions, and the majority of responses to petitions are

    explanatory rather than documentary (CESD, 2009, p. 18).

    The second gap, insight into the decision-making process, is filled explicitly by the

    petitions process, at least for decisions related to environment and sustainable

    development. The petitions process can be used to directly address and question decision-

    making rationales.16

    Since petitions and responses are made publicly accessible, theprocess itself contributes to the creation and publication of the type of information that

    makes decisions transparent.

    In addition to making decisions more transparent by allowing citizens to question the

    rationales and access undocumented information that contributed to them, petitions canbe used to make decision-making processes on the whole more transparent. By drawing

    attention to situations where decisions are consistently opaque, petitioners can encourage

    the government to make the processes more transparent. A petition submitted in 2002dealt with cases in which a recommendation by the Committee on the Status of

    Endangered Wildlife in Canada (COSEWIC) to add a species to the List of Wildlife

    Species at Risk would be ignored (Millls & Wiwcharuk, 2002). At the time, no criteria for

    such decisions were publicly available, and in his response, the Minister stated thatguidelines for such decisions were in development. In 2005, the CESD followed up with

    the Minister, confirming that draft guidelines had been prepared in 2003, presented in

    November 2004, and were to be finalized in 2006 (CESD, 2005, pp. 13-14).

    Whatever the theoretical potential for the Process to enhance transparency in Canada,certain realities suggest that this potential may be limited. With few exceptions, the

    Process goes essentially unmentioned in the academic and institutional literature. The

    plethora of studies on transparency, governance processes, and engagement in sustainable

    14 Art14:2.(b) ;Art1:(a)-(j)15 For examples of referrals to ATIA, see (Whelan, 2002); (Clement, 2007)16 For examples, see (Lischewski & Love, 2005); (Blodgett, 2004)

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    development either ignore or are simply ignorant of the EPP. Beyond the literature, a

    2010 Parliamentary study found that constituents outside of parliament had a low

    awareness of petitions (Stokes, 2010, p. 9). Transparency can only be effective if thereare receptors capable of processing, digesting, and using the information (Heald, 2006,

    p. 35). If the public, academics, and professionals who might effectively make use of the

    information revealed through the process are unaware of it, then the value of its outputsand its overall contribution to transparency may be questionable at best.

    The Commissioners annual petitions report to Parliament ensures the transparency of the

    process itself while enhancing its contribution to transparency in environmental

    governance. The report contains basic information about the quantity of petitions

    received, their subject matter and their status, and highlights emerging issues that attractnumerous petitions issues that might otherwise go unnoticed (Canada, 2010, p. 14).

    17

    The report also includes an audit of the process itself, exposing weaknesses and

    shortcomings. The 2004 report revealed that although departments were committing to

    launch investigations into issues raised by petitions, petitioners were not being informedof the outcomes of these investigations (CESD, 2004, p. 1). It also noted that some

    departments were portraying their petition responses more positively than was warranted.

    These features are similar, though not identical, to other parliamentary petitions

    processes. The Scottish Parliamentary Petitions Committee, for example, has a widerange of actions it can pursue in addressing petitions (Carman C. J., 2006, pp. 2.3-18). It

    submits annual reports and has conducted inquiries into the petitions process, though it

    does not do so annually (Scotland, 2009). It may consult with or request information fromother government bodies, but it has no official mandate to conduct audits.

    The petitions process contributes to transparency by providing citizens with access to

    information, requiring Ministers to respond to the questions and concerns of citizens, and

    making all the information public. The CESD furthers this goal by investigating the

    issues where warranted, analysing and interpreting the results of the process, andexposing its shortcomings to the public.

    However, awareness is not only a problem externally (as mentioned above), but internally

    as well. In a survey of seven Parliamentarians conducted as part of the 2010 study, onlytwo identified petitions as part of the CESD mandate (Stokes, 2010). As was noted in that

    study, this draws into question the value of the contributions made to transparency by the

    tabling of the petitions and the CESDs annual report on petitions. That study noted that

    overall, the visibility of the Commissioners office appears to be low, with poor tomedium understanding of the Offices mandate (Stokes, 2010, p. 9). This may dilute the

    essence the ability of the Commissioner to enhance the contribution of the EPP to

    environmental governance.

    The Environmental Petitions Process provides the public with a mechanism to access awide variety of information, including the rationale for a decision, the process used to

    make decisions, or results and impacts of those decisions. However, though the EPP

    provides that mechanism, there are questions about the extent to which that mechanism is

    17 See, for example (CESD, 2008, p. 7)

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    used. The next section explores how the public engages with the process and the

    information that it makes accessible.

    4.2.Public ParticipationThe Standing Committee on Environment and Sustainable Developments 1994 report

    noted that the public should be given the opportunity to provide input into and to informthe policy debate. In contrast to most public participation mechanisms, which provide forcitizen input into or involvement with a particular project or decision, the Environmental

    Petitions Process is an on-going mechanism that allows the public to participate in the

    general management of the environment and sustainable development in Canada (CESD,2009, p. 1). On Langtons scale, described in Section 2.2, it falls in between Citizen

    Involvement and Citizen Action. Public participation is facilitated by the EPP both by

    improving decision-making processes and by influencing decisions.

    Citizens can directly influence decisions by making explicit comments and suggestions to

    Government on decision-issues, as well as in other ways, for example by requestingreviews and improvements of laws (CESD, 2008). Citizens can also improve the

    decision-making process simply by generating more information for the Government touse. In addition to the downward flow of information created by the transparencymechanism of the EPP, information flows upwards from petitioners to the Government

    and Parliament (CESD, 2009, p. 1). By making known the issues that concern them,

    expressing their opinions on the issues, and providing information relating to them,citizens can improve the information base on which Government makes decisions.

    18

    The developing shale gas issue provides examples of both avenues for participation

    through petitions. As an example of explicit requests influencing decisions, a petition

    received by the Quebec National Assembly dated January 2011 demanded a moratorium

    on shale gas exploration in the province (Anonymous, 2011), which led to the Quebec

    government freezing new exploration and development until a full study on theenvironmental impacts could be completed (Marotte, 2011). Two petitions received by

    the CESD display how information flows upwards from citizens to Parliament andGovernment, improving the decision-making process. Petitions number 307 (Breton,

    2010) and 308 (Bdard, 2010) concerned the federal governments role in regulating the

    shale gas industry in Quebec. These petitions were part of a general public outcry whichled to Parliamentary debate on the matter, and statements by the Environment Minister

    which indicated that the federal government was examining its responsibilities in

    regulating the issue, which would normally fall under provincial jurisdiction (Canada,2011). In the latter case, petitions did not influence a decision, but impacted the decision-

    making process.

    18 For an example of the impact of public participation through petitions, see Military dumpsites off

    Canadas Atlantic coast (CESD, 2004, pp. 14-19)

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    While the flow of information is bidirectional, form citizens to Government (public

    participation) and from Government to citizens (transparency) the impacts of public

    participation are multidirectional (see Figure 1). Petitioners can influence governmentdecision-makers directly, in a bottom-up direction, by making requests and expressing

    their opinions (arrow 1). They can also influence Parliamentary policy-makers in the

    same way, as petitions are tabled annually in Parliament (arrow 2). There is a third flow,

    through the Commissioner of the Environment and Sustainable Development, whoreports annually on the process and provides Parliament with recommendations on the

    governments management of the environment and sustainable development (arrow 3).

    Finally, a fourth direction of influence exists, as petitioners influence on Parliament canbe translated into top-down oversight of government (arrow 4). The multidirectionalinfluences that the EPP offers for public engagement, while enhancing the potential

    impacts of the process, also make it difficult to assess the results it achieves. Though

    anecdotal examples of each can easily be identified, any study attempting to aggregateand assess the overall impacts of the process will have to include a framework that can

    categorize, standardize, identify, and measure the impacts through four directions of

    every petition and response.

    Citizens

    Government

    Parliament

    CESD

    Figure 1 Multi-directional participation & accountability through the Environmental Petitions Proces

    1

    2

    34

    6

    5PoliticalAccountabilit

    ManagerialAccountabilit

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    Again, as with transparency, the process in theory holds great potential to enhance public

    participation in environmental governance in Canada, but the facts on the ground cast

    doubt on its ability to fulfill this potential. Throughout its 15 year history, the CESD hasreceived 350 petitions. The majority of these, however (more than 70%), were received in

    the 6-year period between 2003 and 2008. It is understandable, even to be expected, that

    few petitions might be received in the early years of the process before 2003. Of greaterconcern is the precipitous decline in the number of petitions received since 2008 (seefigure 2). In 2009 only 27 were received, and in 2010 only 19, the fewest in a decade.

    The low number of petitions is cause enough to raise questions about the effectiveness of

    the process: Can the activity of 19 petitioners truly be considered enhanced publicparticipation?

    Figure 2 - Petitions received by the CESD since being established

    If the number of petitions alone isnt enough to cast doubt, the question of what has

    caused the sudden drop is. The peak in petition activity of 2008 was followed by a study

    that found an overall lack of awareness of the process. Since then, petition activity hasdropped by more than half, suggesting a further degradation of awareness. More

    importantly, the drop in activity could be a negative reaction to the perceived(in)effectiveness of the process among the admittedly small community that is evenaware of its existence.

    The CESD enhances public participation in two ways. Firstly, the Commissioner canincrease the effectiveness of public participation through the petitions process by

    highlighting petition topics in the annual reports to Parliament. Doing so heightens the

    visibility of the issues that matter most to petitioners, encouraging relevant ministries toaddress them. Between 2001 and 2007, the Commissioner highlighted 40 petitions in

    annual reports, and action was taken on 35 (CESD, 2007, p. 86). For example, the 2002

    report highlighted the issue of mustard gas and other chemical warfare agents dumped offthe coasts of Nova Scotia and Newfoundland at the end of world war two (CESD, 2002).

    In response, the Minister of National Defence initiated a project to assess the risks

    1 711

    1 6

    17 19

    36 37

    26 28

    41 39

    2315

    25

    68

    69

    5 9

    4

    4

    0

    10

    20

    30

    40

    50

    60

    Petitions to the CESD 1996 - 2010

    Repeat Petitions

    New Petitions

    Number of

    petitions

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    presented by ocean dump sites of warfare agents to the environment and human health

    and to engage in remediation, cleanup or other mitigation measures.

    Secondly, the Commissioner provides an additional opportunity for citizen involvement

    in government scrutiny. If transparency is enhanced by the Commissioner delving deeperinto petition issues, public participation is enhanced by petitioners informing the

    Commissioners work. Audits and studies are powerful tools, and the petitions processpresents an additional opportunity for the public to get involved in the scrutiny ofgovernment entities, plans, policies and programs. The CESD uses the petitions catalogue

    to systematically identify issues for audit, integrating the public into the planning process

    (CESD, 2007, p. 86).

    The right to request an investigation through the Environmental Commissioner ofOntario, though seemingly similar to the integration of petitions in the CESD audit

    function, is in practice quite different. That right is explicitly stated in the Environmental

    Bill of Rights (Environmental Commissioner of Ontario, 2003, p. 22), while the ability to

    influence audits undertaken by the CESD is more implicit. As there is no requirement inthe Auditor General Act to pursue petition topics with audits of the relevant federal

    agencies, the influence that petitions have on the CESD audit program is entirely

    dependent on the extent to which the Commissioner takes petitions into account when

    planning audits. On the other hand, investigations resulting from a request under the EBRare undertaken by the ministry concerned, not an independent audit office. The role of the

    ECO in this case is more akin to the CESD's role in managing the petitions process, and

    is limited to ensuring the request meets minimum criteria and forwarding requests to theappropriate ministry. Canadians are similarly able to request investigations in their

    environmental petitions (CESD, 2008, p. 7), and it is up to the relevant ministries to

    respond to such requests. The result of a CESD audit is more akin to an investigation by

    the New Zealand Parliamentary Commissioner for the Environment, which results inpublicized reports to Parliament with analysis, advice, and recommendations (New

    Zealand, 2011). While the New Zealand Commissioner offers an explicit mechanism to

    Suggest an Investigation, the extent of public participation is not necessarily greater.Just as there is no requirement for the Commissioner to undertake audits of petition topics

    in Canada, there is no guarantee in New Zealand that suggested investigations will be

    undertaken.

    Through the Environmental Petitions Process, citizens can directly influence decisions.The Process is also an avenue for information to enter the decision-making system,

    allowing petitioners not only to make explicit requests but also to inform the Government

    and Parliament about the issues that concern them. Once information has entered thesystem, it flows in many directions. It can impact Government decisions directly, and can

    move Parliament to exert influence on the Government. The CESD can take up the causesof petitioners, highlighting important issues and giving citizens the opportunity to

    influence audit choices.

    4.3.AccountabilitySimilarly to public participation, accountability can be either top-down or bottom-up (seeFigure 1). The mandate of the Office of the Auditor General of Canada includes

    contributing to political accountability (top-down) by providing Parliament with the

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    information it needs to scrutinize the governments performance (OAG, 2004, p. 17). The

    petitions process performs a parallel function for managerial accountability (bottom-up)

    by providing citizens with the information they need to scrutinize the governmentsperformance. While sanctions are not necessary components of accountability systems,

    they can serve to enhance accountability, and citizens control the ultimate sanction.

    Through general elections, they can hold politicians to account, removing from officethose that fail to meet expectations.

    Accountability arises from other consequences of the petitions process as well, including

    what Abels calls accountability communication (Abels, 2007, p. 106). The strength of

    the petitions process is that it goes beyond transparency and provides justifications and

    explanations, responses to specific questions, interpretations, and in some cases,commitments (CESD, 2005, p. 1). The process meets Abels other accountability

    requirements as well it is open to the general public, allows the public to make

    judgements which imply the imposition of sanctions, and deals with matters of public

    interestand as such contributes to the legitimacy of the decision-making system (Abels,2007, p. 106).

    What sets the Canadian process apart from similar processes in enhancing accountability

    is the obligation for departments and agencies to respond. The German and Scottish

    petitions systems, as well as the CEC citizen submissions and many others, offer centralpoints of contact to manage citizens concerns, similar to the Commissioner of the

    Environment and Sustainable Development. Under these other systems, however, though

    the central point of contact may be required to consider the petitions, there is nolegislated requirement that petition issues be investigated or that petitioners receive a

    meaningful response.19

    Whether or not any subsequent actions are taken with regard to a

    petition is left to the discretion of a parliamentary office, the result of which is that these

    bodies offer the potential for, but no guarantee of, accountability. Whereas theseprocesses provide a layer of insulation from accountability, Canadas process is mandated

    and direct. The Commissioner of the Environment and Sustainable Development, the

    central point of contact, ensures that the petitions meet admissibility requirements. If so,neither the CESD nor the department in question decides whether or not a response is

    warranted; a response is mandated in the Auditor General Act, guaranteeing that the

    minister will be held accountable to the public (at least to the extent of providingexplanations and justifications and facing implied consequences).

    Despite the certainty provided by taking discretion out of the equation and mandating a

    response to every admissible petition, the process cannot hold the Government to account

    on its own; rather, it provides a mechanism for the people to do so. Because the thirdpillar is dependent on the first two, the process can only be effective if citizens make use

    of it, and the doubts cast on the value of the transparency offered by the EPP and theextent of the public engagement with it result in doubts about whether it has in fact

    contributed to accountability. The small number of petitions received in recent years not

    19Scotlands and Germanys petitions committees may request responses from relevant parliamentary

    committees or government agencies if they determine such a request is warranted: Regarding Scotland, see

    (Carman C. J., 2006) 2.3.18; Regarding Germany, see (Bundestag Petitions Committee, 1991) 7.14. The

    CEC Secretariat may request a response from a Party if they determine such a request is so warranted, and

    the Party may respond if they wish: See (NAAEC, 1993) Art.14.2 and Art. 14.3.

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    only limits the amount of information being generated by the process, but also suggests

    that too small a portion of the population may be aware of the information generated to

    create meaningful accountability.

    The petitions process contributes to political accountability through the Commissioner ofthe Environment and Sustainable Development, who provides Parliament with the

    information it needs to hold government accountable. In Philps definition ofaccountability, a third party Y holds A accountable to M (Philp, 2009, p. 32). In the caseof environmental petitions, this third party is the CESD. Petitions are addressed to the

    Commissioner, who is responsible for determining the relevant departments and agencies,

    forwarding the petitions, and reviewing responses (CESD, 2008, pp. 8-9). The

    Commissioner can also identify responses that fail to adequately address petitionersconcerns and bring them to the attention of either the responding organization or

    Parliament (CESD, 2008, p. 9).

    As outlined in the two preceding sections, CESD audits augment the petitions process

    with respect to transparency and public participation, and the same is true foraccountability. The Commissioner does not investigate or substantiate the claims made in

    every departmental response (CESD, 2008, p. 8), but does validate those claims when an

    audit covers an issue on which petitions have been submitted, as well as on a sample

    basis in annual reports. In 2007, the Commissioner wrote that the Office wassystematically using petitions to identify issues for audit (CESD, 2007, p. 86).

    In those cases, Ministers, departments and agencies are held accountable to the

    commitments they have made to the public. In keeping with the definitions of

    accountability found in Section 3, though the Commissioner cannot issue bindingsanctions or rewards, his work implies the possibility of sanctions and rewards because it

    provides the public and Parliament with the raw information it needs to judge the

    Governments performance. Where departments are effectively addressing issues raised

    in petitions, their success is reported to Parliament and the public. Conversely, wheredepartments are failing or where there is room for improvement, the Commissioner

    makes recommendations to Parliament on what can and should be done better.

    In 2004, for instance, the Commissioner conducted audits of strategic environmentalassessment and the management of salmon fisheries. Petitions related to both those issues

    had been received in the past, and the audits provided an opportunity for the

    Commissioner to verify the responses to those petitions. The Commissioner found that in

    the case of environmental assessments, most departments were not making serious effortsto apply cabinet directives, and in the case of the fisheriess that Fisheries and Oceans

    Canada had missed all the timelines to which it had committed (CESD, 2004).

    The Environmental Petitions Process gives both Parliamentarians and citizens theinformation they need to hold the Government accountable. It mandates that Ministersrespond to questions about their rationales and processes, the decisions they make, and

    the impacts and results of those decisions. Both the CESD and petitioners can follow up

    to hold the Government to account for commitments made through the Process. Overall,

    the Process enhances the third pillar by subjecting the Government to the first two: bycombining the information it makes accessible through its transparency mechanisms with

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    the actions it makes possible through its public participation mechanisms. In this way, all

    three intertwine, depending on and building on each other.

    5. ConclusionsThe Environmental Petitions Process, as shown in this paper, has the potential to enhance

    what the academic and international communities have identified as the bases foreffective environmental governance: transparency, public participation, andaccountability. It was established as the culmination of years of international progress and

    a thorough Parliamentary legislative process. It is both surprising and unfortunate that it

    has not been the subject of critical analysis until now, and that it is scarcely mentioned inthe media and academia.

    The process can enhance transparency by complementing the Access to Information Act

    and giving citizens the right to access not only documentary information but also

    governmental views and positions, explanations, and decision-making rationales. Making

    the decisions transparent and accessible can increase their legitimacy and provide amechanism for holding the government accountable. The Commissioner of the

    Environment and Sustainable Development can further enhance transparency by auditingpetition subjects and petitioned agencies and providing independent analysis andinterpretation of the results of the process.

    The ways in which the process contributes to public participation can be placed into two

    categories. Citizens can make explicit requests or demands in the hopes of directly

    influencing decisions taken by government, most closely aligned with the Citizen Actionconception of public participation. More closely aligned with the Citizen Involvement

    conception of public participation, citizens can improve the decision-making process by

    making known the issues that concern them and their opinions on those issues,

    contributions that are aggregated in the Commissioners annual reports. Citizens can also

    have a direct impact on the work undertaken by the Commissioner, and the annual reportfurther enhances the impacts of public participation by highlighting the emerging issues

    most deserving of Parliamentary attention.

    By increasing transparency and fostering public participation, the process enhancesgovernment accountability. It provides citizens with the information they need to

    scrutinize governments performance, going beyond transparency to allow citizens to ask

    specific questions, and mandating that the petitioned agencies respond. This allows thepublic to make judgements which imply the imposition of sanctions. In a parallel fashion,

    the Commissioner provides Parliament with the information it needs to scrutinize

    governments performance and hold it accountable. The CESD can identify responsesthat fail to meet requirements, verify and follow up on claims and commitments made in

    response to petitions, and conduct audits and studies where necessary to hold governmentto account.

    The EPP is a petitions process in the style of Scotland and Germany through which the

    public can ask questions, make complaints, suggest improvements, and get responses oractions yet it is the only petitions process dedicated solely to matters of environment

    and sustainable development. Housing it within the Office of the Auditor General under

    the aegis of the CESD creates an independent investigator in the style of the CEC, and

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    the audit function gives it teeth more similar to New Zealands Parliamentary

    Commissioner for the Environment. Where other petitions committees refer

    investigations to the ministries being questioned, CESD audits are independent andobjective, with a mandate to identify shortcomings and inefficiencies. The process

    straddles the lines between passive and active transparency; between the sunshine laws so

    effective in Sweden and the regulatory disclosure found in the United States and Canada;and between citizen action controlled by the public, and citizen involvement initiated bygovernment.

    With the exception of the 2010 study, where the process has been examined it has been

    lauded. Federal department officials have said they believe that the petitions process has

    had an impact on the federal management of environmental and sustainabledevelopment issues (CESD, 2007, p. 87). In providing recommendations for reshaping

    environmental governance in Northern Ireland, Macrory suggests that governments can

    enhance public influence and connection with government bodies by instituting a

    petition system, under the auspices of the Audit body, along the lines of the Canadianmodel (Macrory, 2004, p. 43). However, these instances are few, and as such,

    inconclusive.

    The purpose of this paper was to examine how the process might contribute to

    environmental governance as was intended, and it is clear from this examination that, asdesigned, it has the potential to do so. There is anecdotal evidence in the form of

    individual petitions to suggest that they do have the intended effects: A petition on

    military off-shore dump sites resulted in commitments by the Minister of NationalDefence to assess and clean up those sites; Audits conducted by the CESD have

    uncovered instances where Departments have failed to follow through on their

    commitments to petitioners; A petition regarding the requirements for EIAs in a housing

    development in British Columbia elicited new information from the Department ofFisheries and Oceans about its responses to proposals by the proponent.

    However, there is as yet no evidence that the process as a whole has fulfilled its potential.

    Despite the anecdotal evidence, it is unclear what proportion of petitions has had the

    intended impacts of enhancing transparency, public participation, or governmentaccountability. In fact, if there is any evidence as to the actual achievements of the

    process, they may point to the contrary. The only data available about the process are the

    raw numbers of petitions received over the years: 350 in total, nearly 70% of which werereceived in the six years between 2003 and 2008, after which the number drops by half in

    only two years, despite increasing outreach efforts by the CESD. Without more data to

    analyze, the implication is that the process is so unknown, so little used, that even ifevery petition submitted achieved each of the objectives for the process, the results might

    still be inconsequential in terms of a significant national impact.It is impossible to say what impacts the 19 petitions received in 2010 have had. Take for

    example the issue of shale gas development in Quebec. It is true that petitions on the

    topic were received at both the provincial and federal levels; that the provincial petitiondemanded a moratorium on exploration and was followed by a freeze on exploration until

    environmental studies were conducted; and that the federal petitions questioned the

    federal governments role and were followed by Parliamentary debate and statements bythe Minister suggesting that the federal government was examining its role vis--vis

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    provincial jurisdiction. However, it is also true that the shale gas issue was popularized in

    the mass media, was taken up by a number of citizen groups and NGOs, was recognized

    at international levels, and that significant impacts had already been seen in otherjurisdictions.

    20Without more careful study, it is impossible to attribute the actions of the

    provincial and federal governments directly, or solely, to the petitions. This is but one

    example of the difficulties posed in measuring the actual achievements of the process.

    6. Recommendations for Further ResearchThe initial goal of this paper was to assess whether the Environmental Petitions Process

    has met its objectives. After identifying the objectives of the process to contribute tosustainable development in Canada by improving environmental governance I

    proceeded to identify suitable indicators and build a framework around them. These

    indicators, transparency, public participation and accountability, engaged in complex

    relationships and were not directly measurable. As a result, before an empiricalassessment would be possible, it was necessary to evaluate in what ways and through

    what mechanisms the EPP could contribute to those three pillars. Due to a dearth in the

    literature of evaluation or exploration of the petitions process, this paper has been aprimary attempt to critically examine its design, its intentions, and its potential. The next

    step