Date:
20131031
Docket:
T-888-10
Citation:
2013 FC 1112
Maniwaki,
Québec, October 31, 2013
PRESENT: The Honourable Madam Justice Heneghan
BETWEEN:
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SANDY POND ALLIANCE TO PROTECT
CANADIAN WATERS INC.
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Applicant
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and
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HER MAJESTY THE QUEEN IN RIGHT
OF CANADA AS REPRESENTED BY THE ATTORNEY GENERAL OF CANADA
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Respondent
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and
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VALE INCO LTD., MINING
ASSOCIATION OF CANADA AND MINING ASSOCIATION OF BRITISH COLUMBIA
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Interveners
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REASONS FOR
JUDGMENT AND JUDGMENT
I. INTRODUCTION
[1]
Sandy
Pond Alliance to Protect Canadian Waters Inc. (the “Applicant”) commenced this
application for judicial review pursuant to section 18.1 of the Federal
Courts Act, R.S.C. 1985, c. F-7 and the Federal Courts Rules,
SOR/98-106 (the “Rules”), seeking a declaration that the regulatory scheme set
out in sections 5 and 27.1 and Schedule 2 of the Metal Mining Effluent
Regulations, SOR/2002-222 (the “2002 MMER” or the “2002 Regulations”), as
amended by the Regulations Amending the Metal Mining Effluent Regulations,
SOR/2006-239 (the “2006 MMER” or “2006 Regulations”) are ultra vires the
regulation-making powers granted to the Governor in Council pursuant to the
provisions of the Fisheries Act, R.S.C. 1985, c. F-14 (the “Fisheries
Act” or the “Act”).
[2]
In
its application for judicial review the Applicant seeks the following relief:
3. The applicant makes application for: Declaratory
Relief as follows:
(a) A declaration that
the following sections of the Metal Mining Effluent Regulations,
SOR/2002-222 as amended are unlawful as being contrary to the Fisheries Act
[R.S., c. F-14, s. 1] and ultra vires the authority granted to the
Governor in Council pursuant to the Fisheries Act and subsections 34(2),
36(5) and 38(9) of the Fisheries Act, and are hereby declared to be of
no force and effect:
i. SCHEDULE 2 of
the Metal Mining Effluent Regulations
ii. Section 5 of the
Metal Mining Effluent Regulations
iii. Section 27.1 of
the Metal Mining Effluent Regulations
4. That in the alternative to (a)
above, a declaration that the Governor in Council acted beyond its jurisdiction
or without jurisdiction in issuing SOR/2006-239, October 3, 2006 and creating
SCHEDULE 2, Section 5 and Section 27.1 of the Metal Mining Effluent
Regulations.
II. THE
PARTIES
A)
The Applicant
[3]
The
Applicant is a not-for-profit corporation created and existing under the laws
of Newfoundland and Labrador. It describes its aims and objectives:
a.
To
protect and conserve Canadian waters and their ecosystems; and
b.
To
take appropriate actions to assist the Alliance in fulfilling its purpose,
including promoting and recommending laws and policies, and informing and
engaging the public; and
c.
To
join and/or co-operate with other organizations or institutions with similar
purposes.
[4]
The
Applicant is a public interest litigant.
[5]
Her
Majesty the Queen in Right of Canada as Represented by the Attorney General
(the “Respondent”) is the Respondent.
[6]
Vale
Inco Ltd. (“Vale”) is a Canadian company with extensive and significant mining
operations throughout Canada. Vale Inco Newfoundland and Labrador Limited is a
wholly owned subsidiary of Vale, operating a plant at Long Harbour, Placentia Bay, Newfoundland and Labrador. The Long Harbour operations involve a nickel
processing plant (the “Project”). That plant will generate residue known as “tailings”
which will require a tailings impoundment area (“TIA”). Nineteen TIAs are
described in Schedule 2 of the Regulations by their geographic coordinates.
[7]
The
Mining Association of Canada (the “MAC”) is a national organization for the
Canadian mining industry. It has existed since 1935 and was initially known as
the “Canadian Metal Mining Association”. It represents most of the mining
operations currently listed in Schedule 2 of the MMER.
[8]
The
Mining Association of British Columbia (the “MABC”) was created in 1901
pursuant to an act of the province of British Columbia. It is the dominant
voice of the mining industry in British Columbia. Its members are engaged in
metal and coal mining in British Columbia and internationally.
[9]
Vale,
the MAC and the MABC sought status in this proceeding as either Interveners or
Respondents, pursuant to the Rules. By Order issued on February 10, 2011, those
three parties were granted status as Interveners, upon certain terms and conditions:
see Sandy Pond Alliance to Protect Canadian Waters Inc. v. Canada (Attorney General), 2011 FC 158.
[10]
By
Notice of Appeal filed on February 18, 2011, the MAC and the MABC appealed
against that Order. By Judgment dated April 9, 2011, the appeal was allowed in
part, to afford the MAC and the MABC the right to file affidavits from two
expert witnesses, in addition to the affidavits previously filed, and the right
to participate in cross-examination of the deponents for the Applicant and the
Respondent. The Federal Court of Appeal sustained the status of Vale, the MAC
and the MABC as Interveners: see Sandy Pond Alliance to Protect Canadian
Waters Inc. v. Canada (Attorney General) (2011), 418 N.R. 55.
B) The Evidence
[11]
The
evidence of the parties was entered by way of affidavit, the usual manner of
submitting evidence in an application for judicial review.
[12]
The
Applicant submitted the affidavit of Dr. John Gibson, a retired marine
biologist and a former employee of the Department of Fisheries and Oceans
(“DFO”) Canada. This affidavit was sworn to on June 4, 2010.
[13]
The
Applicant sought leave to file a further affidavit, sworn to on June 23, 2011,
as a rebuttal to the affidavits filed by the other parties and in support of
his affidavit dated June 4, 2011. By Order of Prothonotary Aronovitch, dated
November 11, 2011, leave to file the further affidavit was denied on the basis
that the Applicant had failed to meet the criteria applicable to the filing of
supplementary evidence.
[14]
In
disposing of the Applicant’s motion to file a further affidavit of Dr. Gibson,
Prothonotary Aronovitch remitted the issue of qualifying Dr. Gibson as an
expert witness to the judge hearing the case on the merits. That issue will be
addressed below.
[15]
The
Respondent filed the affidavits of Mr. Marvin A. Barnes and Mr. Chris Doiron.
Mr. Barnes is employed with DFO and at the time of swearing his affidavit, was
the Regional Manager, Environmental Assessment and Major Projects; Ocean,
Habitat and Species at Risk Branch. In that capacity he was involved with and
responsible for environmental assessments of major development projects
pursuant to the Canadian Environmental Assessment Act, S.C. 1992, c. 37
(the “CEAA”), a statute that was repealed in 2012. The Project at Long Harbour, together with the designation of Sandy Pond as a TIA, was subject to review
under the CEAA.
[16]
Mr.
Barnes described the steps that were taken from March 2006, when DFO received a
Project Description from the Canadian Environmental Assessment Agency (the
“Agency”) until July 2008 when the Agency gave notice of its Decision that the
Project was unlikely to cause significant adverse environmental effects.
[17]
These
steps included a request from the Province of Newfoundland and Labrador to DFO
for an opinion on the Project Description; preparation of an Environmental
Impact Statement (“EIS”) by Vale and its submission to DFO and Transport Canada
(“TC”) by Vale; a request to amend the Regulations to include hydrometallurgical
(“hydromet”) plants such as the proposed Project and the use of Sandy Pond as a
residue management and storage site; the submission of the final Fish Habitat
Compensation Strategy for Sandy Pond and Notification from DFO that the
strategy was acceptable pursuant to section 27.1 of the Regulations; and two
public consultation sessions, one in Long Harbour, Newfoundland and Labrador
and the second in Gatineau, Québec.
[18]
Mr.
Chris Doiron is an employee of Her Majesty the Queen in Right of Canada as
Chief of the Mining Section, Mining and Processing Division, at Environment Canada.
He has held that position since May 2004. In that capacity he was engaged in
the evaluation of the proposed waste disposal facility at Sandy Pond by the
Voisey’s Bay Nickel Company Limited, as part of the Project.
[19]
In
his affidavit, dated July 29, 2010, Mr. Doiron described the steps undertaken
by the federal regulatory authorities between 2005 and 2008 leading up to the
amendments by which Sandy Pond was added to Schedule 2, effective May 28, 2009.
DFO and TC were involved in the process leading up to the amendments to the
Regulations due to their status as “responsible authorities” within the scope
of the CEAA. He deposed that he was integrally involved with Environment Canada’s
supervision of the regulatory process leading up to the 2009 listing of Sandy
Pond as a TIA in Schedule 2 and the expanded scope of the Regulations to
include hydromet facilities. This process led to the enactment of the Regulations
Amending the Metal Mining Effluent Regulations, SOR/2009-156 (the “Voisey’s
Bay MMER Amendments”).
[20]
The
MAC and the MABC filed the affidavit of Elizabeth J. Gardiner and the reports
of Dr. Dirk Jacobus Albertus Van Zyl and Dr. Eric B. Taylor, as expert
witnesses.
[21]
Ms.
Gardiner is the Executive Advisor for the MAC. She was Vice-President,
Technical affairs for that organization, from 1996 until 2010. In her
affidavit, dated May 6, 2011, she addressed the role of the MAC as the national
organization for the Canadian mining industry and its engagement in the pursuit
and maintenance of high standards of environmental performances and management.
She commented on the evolution of the federal regulatory scheme beginning in
the 1990s and leading up to the introduction of the MMER in 2002, including the
introduction of Schedule 2. She also addressed the 2006 amendments, notably the
addition of section 27.1.
[22]
The
MAC and the MABC also filed the reports of two expert witnesses, Dr. Van Zyl
and Dr. Taylor. Each of these reports was accompanied by a Certificate
concerning the “Code of Conduct for Expert Witnesses” pursuant to Rule 52.2 of
the Rules.
[23]
Dr.
Van Zyl is a civil engineer. His report addresses the production and management
of tailings, that is residue left after the recovery of metal in a mineral
processing facility. His report talks about the options for the management of
tailings, either on land surface, below land surface and under water and
provides some comparison of the advantages and disadvantages of each option.
[24]
The
second report, from Dr. Taylor, is entitled “Adaptive radiation and Sandy Pond
Brook Trout”. Dr. Taylor, currently a professor of zoology at the University of British Columbia, commented on an article written by Dr. Gibson, entitled
“The inequity of compensation for destroyed lakes”. Dr. Taylor disputed the
opinion offered by Dr. Gibson as to the “adaptive evolution” of Sandy Pond
Brook Trout.
[25]
Vale
filed the affidavits of Mr. Don Stevens, Ms. Margarette Livie, Ms. Macijie B.
Szymanski and Mr. James H. McCarthy, as well as the transcript of the
cross-examination of Dr. Gibson.
[26]
Mr.
Stevens swore two affidavits, the first on July 13, 2010, and the second on May
6, 2011. Mr. Stevens is the General Manager of the Vale plant in Long Harbour. In his affidavits he stated that at Vale’s request, Schedule 2 of the
Regulations was amended to list Sandy Pond as a TIA. He also reviewed the steps
that Vale followed leading up to the amendment of the Regulations.
[27]
Ms.
Livie swore an affidavit on July 27, 2010. At that time, she was a law clerk to
Counsel for Vale. She attached certain documents as exhibits to her affidavit,
including a transcript of a radio broadcast, a copy of a “background document”
about the Applicant, documents relating to the incorporation of the Applicant, and
a transcript of a television news story. Her evidence is submitted for the
purpose of showing that the Applicant is focusing solely on the Long Harbour facility and Sandy Pond. Vale also relies on the affidavit for the purpose of
challenging the status of Dr. Gibson as an expert witness.
[28]
Ms.
Szymanski, a professional engineer, was retained by Vale to provide an expert
report. Her report is accompanied by a certificate pursuant to Rule 52.2 of the
Rules.
[29]
Ms.
Szymanski is employed with AMEC Earth and Environmental Projects, Mining
Projects, and experienced in the selection and design of TIAs for mining
projects. In her expert report, she commented upon the steps taken by Vale
leading up to the selection of Sandy Pond as the desired TIA.
[30]
Vale
filed a second expert report, that is the report of Mr. James H. McCarthy. He
is a senior biologist employed with AMEC Earth and Environmental Projects. He was
mandated to provide an opinion about the compensation plan for Sandy Pond,
including background information about the assessment of fish and fish habitat
and the plan itself. He provided a certification confirming compliance with the
Code of Conduct for Expert Witnesses pursuant to Rule 52.2 of the Rules.
III. SUBMISSIONS
A) The Applicant
[31]
The
Applicant challenges certain provisions of the 2002 Regulations, as amended in
2006, specifically, section 5, section 27.1, and Schedule 2, on the grounds
that these provisions are ultra vires the authority conferred on the
Governor in Council to make regulations pursuant to the Fisheries Act. It
submits that these regulatory amendments are not authorized by the Fisheries
Act, and in any event that the Regulations contravene the statutory purpose of
conserving and protecting Canadian fisheries, including inland fisheries in
fresh waters.
[32]
The
Applicant argues that the regulatory scheme set out in the 2002 version of the
Regulations is proper, legal and vires the regulation-making powers set
out in the Fisheries Act because those Regulations required the treatment of
effluent prior to its discharge into water bodies so its ultimate discharge
would not harm or destroy fish and other life-forms. In this regard, the
Applicant relies on the Regulatory Impact Analysis Statement that
accompanied the 2002 Regulations.
[33]
The
Applicant submits that the 2006 amendments to the Regulations, as illustrated
by section 5 and section 27.1, eliminated this protection and now allows the
discharge of effluent without prior treatment, thereby creating the potential
for the destruction of fish, fish habitat and other life-forms. It submits that
this regime is contrary to the conservation purposes anticipated by the Act.
[34]
The
Applicant submits that the amendments represent a significant change from the
prior regulation of the discharge of effluents and that this significant change
should be specifically authorized by some provision in the Fisheries Act. It
refers to section 7 of the Act that confers full discretion upon the Minister of
Fisheries and Oceans (the “Minister”) over the granting of licences and submits
that a similar legislative authority should be spelled out in the Act to
authorize the passage of regulations that can kill off fish and fish habitat.
[35]
In
the absence of such a specific statutory provision, the Applicant argues that
there is no “statutory foundation” to allow the Governor in Council to make the
2006 amendments to the 2002 iteration of the Regulations.
B) The Respondent
[36]
The
Respondent takes the position that the amendments are within the existing
powers conferred by the Act. He notes that the amendments in issue specifically
refer to subsection 36(5). He submits that the scheme of the Act contemplates
the authorization of the deposit of deleterious substances in fish-bearing
waters, subject to the Regulations.
[37]
The
Respondent further submits that the Act contemplates both the deposit of
deleterious substances in fish-bearing waters, as well as the preservation of
fish spawning grounds and fish habitat. He relies on the observations of the
Federal Court of Appeal in Georgia Strait Alliance et al. v. Canada (Minister of Fisheries and Oceans) et al. (2012), 427 N.R. 110 where that Court
said the following at paragraph 127:
Subsection 35(1) of the Fisheries Act
prohibits any work or undertaking that results in the harmful alteration,
disruption or destruction of fish habitat. However, subsection 35(2) allows the
Minister to authorize the alteration, disruption or destruction of fish habitat
under any conditions he deems appropriate. The prohibitions set out in
subsection 35(1), when read in conjunction with subsection 35(2), thus
constitute a legal means whereby the Minister is enabled to manage and control
the alteration, disruption or destruction of fish habitat. In other words,
subsection 35(2) allows the Minister to issue a permit to a person to engage in
conduct harmful to fish habitat that would otherwise contravene subsection
35(1): Quebec (Attorney General) v. Moses, 2010 SCC
17, [2010] 1 S.C.R. 557 at para. 49.
[38]
The
Respondent focuses on subsection 36(5) of the Act as being the critical
provision of the Act for the purposes of the Applicant’s challenge. He says
that this provision allows the Governor in Council to make regulations
authorizing the deposit of deleterious substances. He highlights the difference
between subsection 36(5) and subsection 35(2) which authorizes activities
resulting in the destruction of fish habitat, pursuant to certain conditions.
Under subsection 35(2), authorization is required from the Minister, a
prescribed person or conditions, or another provision in the Act for a work
resulting in the destruction of fish habitat. Subsection 36(5) allows such
deposit pursuant to regulation rather than by authorization.
[39]
In
brief, the Respondent submits that management of the fisheries resources has
allowed the deposit of deleterious substances. The current Regulations are
authorized pursuant to subsection 36(5) and are consistent with the statutory
scheme, as confirmed in the decision of Ecology Action Centre Society
v. Canada (Attorney General) (2004), 262 F.T.R. 160.
[40]
The
Respondent further submits that prior to the 2002 Regulations, fish-bearing
waters could only be used for the deposit of deleterious substances pursuant to
an authorization issued under subsection 35(2) of the Act. The current
Regulations provide a different mechanism to do the same thing.
[41]
The
Respondent also highlights that Sandy Pond was added to Schedule 2 in 2009 but
Schedule 2 itself was created as a result of the 2002 Regulations. The addition
of Sandy Pond to Schedule 2 in 2009 is to be assessed subject to sections 5 and
27.1 which are new; these provisions did not exist under the 2002 Regulations.
[42]
The
Respondent argues that the only difference between the 2002 Regulations and the
2006 amendments is that “tailings impoundment area” is defined in the
definition section of the 2002 Regulations but is incorporated in subsection
5(1) of the 2006 Regulations. Otherwise, the Regulations are the same and since
the Applicant has no quarrel with the validity of the 2002 Regulations, its
challenge to the 2006 amendments is without merit.
[43]
Finally,
the Respondent submits that the amendments to the Fisheries Act in 2012,
pursuant to Bill C-38, An Act to implement certain provisions of the budget
tabled in Parliament on March 29, 2012 and other measures, 1st
sess, 38th Parl, 2012, do not affect the 2006 Regulations. The Regulations
were amended in 2009 to cover hydromet plants, a new type of metal processing
technology which is utilized by the Project at Long Harbour. Details about this
technology are reviewed in the affidavits of Mr. Barnes and Mr. Doiron.
C) The Interveners
[44]
The
MAC and the MABC support the position advanced by the Respondent. They emphasize
that the Fisheries Act does not contain a purpose provision that is
specifically directed to the conservation and protection of fish and submit
that in the absence of such a provision the scope of the Act should not be
restricted as having only one narrow purpose. They refer to the history of the
Act since its inception in 1868 and argue that from the beginning, Parliament
exercised a broad discretion over the management of fisheries resources, having
regard to the competing demand of industry and the need to manage the resource.
[45]
The
MAC and the MABC refer to and rely on recent decisions that confirm the broad scope
of Parliament’s jurisdiction over the fisheries including the decision in Ward
v. Canada (Attorney General), [2002] 1 S.C.R. 569.
IV. DISCUSSION
AND DISPOSITION
[46]
There
are two matters that merit comment, as preliminary matters. The first is the
status of the Applicant as a public interest litigant and the second is the
status of Dr. Gibson as an expert witness.
[47]
The
Applicant is a not-for-profit corporation that was incorporated solely for the
purpose of bringing this application. Although no party has questioned its
ability to pursue this litigation, it is appropriate to address its standing.
[48]
In
Moresby Explorers Ltd. et al. v. Canada (Attorney General) et al. (2006),
350 N.R. 101 at paragraph 17 the Federal Court of Appeal commented on public
interest standing as follows:
Standing is a device used by the courts to
discourage litigation by officious inter-meddlers. It is not intended to be a
pre-emptive determination that a litigant has no valid cause of action. There
is a distinction to be drawn between one's entitlement to a remedy and one's
right to raise a justiciable issue.
[49]
I
am satisfied that the Applicant enjoys status as a public interest litigant for
the purpose of this proceeding.
[50]
I
now turn to Dr. Gibson, a marine biologist who was put forward by the Applicant
as an expert witness. The evidence of Dr. Gibson, submitted by the Applicant,
was the subject of argument during the hearing. Counsel for the Respondent,
Vale, the MAC and the MABC vigorously disputed the recognition of Dr. Gibson as
an “expert witness”, that is, a person recognized by the Court as being
qualified to offer opinion evidence on the matters in issue.
[51]
Various
objections were raised by these parties including the participation of Dr.
Gibson in the incorporation of the Applicant, his status as a Director of the
Applicant, his role as a fundraiser on behalf of the Applicant, and his
admission upon cross-examination, that he considered himself as an “advocate”
for the Applicant.
[52]
The
role of Dr. Gibson as an “expert witness” was raised when the Applicant sought
leave to file his further affidavit. In dismissing the motion in that regard,
Prothonotary Aronovitch reserved to the trial judge a determination of his
status. This was addressed at the outset of the hearing.
[53]
Specifically,
exception was taken to paragraphs 7 to 15 of his affidavit, as follow:
7. In my opinion this is a serious weakening of the
conservation function of the Fisheries Act.
8. Subsequently I wrote an article expressing my
concerns about the amended (sic) the Metal Mining Effluent
Regulations entitled: “The Inequity of Compensation for Destroyed Lakes” [The Osprey, 41(3), 2010 (In Press)] and it is attached to this my affidavit
as Exhibit “B”.
9. Another article I wrote on the same subject was
published in the Canadian Society of Environmental Biologists Newsletter/Bulletin,
Volume 67, No. 1, Spring 2010, p 12 and it is attached to this my affidavit as
Exhibit “C”.
10. I am concerned about the ecological implications
of the amendments to the Metal Mining Effluent Regulation (sic)
in 2006 and in particular the creation of the regulatory scheme that allows
natural freshwater ecosystems such as Sandy Pond, Newfoundland and Labrador
(located at 47˚25’33” north latitude and 53˚46’52” west longitude, on
the Avalon Peninsula, approximately 3 km east southeast of the town of Long
Harbour-Mount Arlington Heights, Newfoundland and Labrador) to be classified as
tailings impoundment areas for industrial mining effluent waste.
11. That the proposed discharge of toxic substances
permitted by amendments to the Metal Mining Effluent Regulation (sic)
will result in all life in Sandy Pond being extirpated.
12. That Sandy Pond is a unique ecosystem which once
lost can not be recreated.
13. It is my opinion that the loss of Sandy pond will cause major losses of fish habitats and biological diversity, as well as
removing recreational opportunities.
14. That I am familiar with the compensation scheme
contained at section 27.1 of the Metal Mining Effluent Regulations and
it is my opinion that adequate compensation for the destruction of a whole
ecosystem, such as Sandy Pond, is in fact impossible.
15. That traditionally mining companies built their
own tailings ponds, and this should be the norm, rather than allowing
destruction of waters containing fish pursuant to a Schedule 2 listing in the Metal
Mining Effluent Regulations.
[54]
After
hearing the submissions of Counsel, a ruling was made that Dr. Gibson would not
be recognized as an “expert” witness. Although the Respondent and Interveners
requested that his affidavit be struck out, the ruling provided that the
impugned paragraphs be given no weight, on the basis that they were expressions
of a personal opinion rather than of a scientific opinion.
[55]
In
Fraser River Pile and Dredge Ltd. v. Empire Tug Boats Ltd. et al.(1995),
95 F.T.R. 43, Justice Reed reviewed the characteristics of “expert evidence” as
evidence from a person who is knowledgeable about the litigation issues and
whose evidence may be necessary to allow the trier of fact to understand the
evidence. His evidence, as set out in the paragraphs quoted above, does not
meet the test for expert opinion and is subject to the criticism levelled by
Justice Reed in Fraser River at paragraphs 14 and 17.
[56]
In
the result, the above paragraphs will remain but will be given no weight in the
disposition of this application.
[57]
At
the same time, I acknowledge and endorse the submissions of Counsel for the
Respondent and the Interveners that no issue is taken with Dr. Gibson’s
education, experience, qualifications, and sincerity. His evidence is rejected
because it does not meet the legal test for expert evidence, that is relevance
and necessity as discussed in Fraser River, at paragraphs 10 and 14.
[58]
This
application is a challenge to the authority of the Governor in Council to enact
sections 5 and 27.1 of the 2006 MMER, as well as a challenge to the creation of
Schedule 2 by the 2002 MMER as subsequently amended.
[59]
The
issue here is whether the 2006 amendments to the Regulations are authorized by
statute. This issue is reviewable on the standard of correctness; see Canadian
Council for Refugees v. Canada, [2009] 3 F.C.R. 136 at para. 63. The issue
of law in this application is not the interpretation of sections 5 and 27.1 of
the 2006 Regulations but whether those provisions, together with Schedule 2 of
the 2002 Regulations, were validly enacted.
[60]
The
Federal Parliament enjoys exclusive legislative authority over the fisheries
in Canada pursuant to subsection 91(12) of the Constitution Act, 1867 (UK), 30 & 31 Vict., c. 3 which provides as follows:
|
91. It shall be lawful for the Queen, by and with
the Advice and Consent of the Senate and House of Commons, to make Laws for
the Peace, Order, and good Government of Canada, in relation to all Matters
not coming within the Classes of Subjects by this Act assigned exclusively to
the Legislatures of the Provinces; and for greater Certainty, but not so as
to restrict the Generality of the foregoing Terms of this Section, it is
hereby declared that (notwithstanding anything in this Act) the exclusive
Legislative Authority of the Parliament of Canada extends to all Matters
coming within the Classes of Subjects next hereinafter enumerated; that is to
say,
[…]
12. Sea Coast and Inland
Fisheries.
|
91. Il sera loisible à la
Reine, de l’avis et du consentement du Sénat et de la Chambre des Communes,
de faire des lois pour la paix, l’ordre et le bon gouvernement du Canada,
relativement à toutes les matières ne tombant pas dans les catégories de
sujets par la présente loi exclusivement assignés aux législatures des
provinces; mais, pour plus de garantie, sans toutefois restreindre la
généralité des termes ci-haut employés dans le présent article, il est par la
présente déclaré que (nonobstant toute disposition contraire énoncée dans la
présente loi) l’autorité législative exclusive du parlement du Canada s’étend
à toutes les matières tombant dans les catégories de sujets ci-dessous
énumérés, savoir :
[…]
12. Les pêcheries des côtes de
la mer et de l’intérieur.
|
[61]
As
noted in the submissions of the MAC and the MABC, legislation governing the
fisheries has existed for nearly as long as the country, the first Fisheries
Act having been passed in 1868. Litigation has ensued since the late nineteenth
century regarding the interpretation and scope of the federal government’s
power over the fisheries; see Reference re: Provincial Fisheries, [1898]
A.C. 700; British Columbia (Attorney General) v. Canada (Attorney General),
[1914] 15 D.L.R. 308; and Quebec Fisheries (Re), [1921] 56 D.L.R. 358.
[62]
With
the exception of the opinion expressed in the affidavit of Dr. Gibson filed by
the Applicant, there is no challenge in this proceeding to the manner in which
Sandy Pond was chosen by Vale and approved by DFO as a TIA, nor to the elements
of the compensation plan that was proposed by Vale and accepted by DFO.
[63]
There
is little scope for a reviewing Court to comment on such matters since the
choice of science is recognized as a matter properly falling within the powers
of the governing authority, pursuant to the applicable legislation. In this
regard, I refer to the decision in Inverhuron & District Ratepayers’
Association v. Canada (Minister of the Environment) et al. (2001), 273 N.R.
62 at paragraph 48. The evidence tendered by the Respondent and the Interveners
adequately establishes a factual background relating to the establishment and
function of a TIA, the choice of Sandy Pond as a TIA and the compensation plan
required under the Act.
[64]
The
preamble to the 2002 Regulations reads as follows:
|
Her Excellency the Governor General in Council, on the
recommendation of the Minister of Fisheries and Oceans, pursuant to subsections
34(2), 36(5) and 38(9) of the Fisheries Act, hereby makes the annexed Metal
Mining Effluent Regulations.
|
Sur
recommandation du ministre des Pêches et des Océans et en vertu des
paragraphes 34(2), 36(5) et 38(9) de la Loi sur les
pêches, Son Excellence la Gouverneure générale en conseil prend
le Règlement sur les effluents des mines de métaux, ci-après.
|
[65]
The
preamble to the 2006 Regulations reads as follows:
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Her Excellency the Governor General in Council, on
the recommendation of the Minister of Fisheries and Oceans, pursuant to
subsections 36(5) and 38(9) of the Fisheries Act, hereby makes the annexed Regulations
Amending the Metal Mining Effluent Regulations.
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Sur recommandation du ministre
des Pêches et des Océans et en vertu des paragraphes 36(5) et 38(9) de la Loi
sur les pêches, Son Excellence la Gouverneure générale en conseil prend le Règlement
modifiant le Règlement sur les effluents des mines de metaux,
ci-après.
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[66]
The
Applicant argues that the challenged Regulations are ultra vires the
power of the Governor in Council because they offend against the conservation
purposes of the Act. In this regard, the Applicant relies on section 7 of the
Act and the decision of the Supreme Court of Canada in Comeau’s Sea Foods
Ltd. v. Canada (Minister of Fisheries and Oceans), [1997] 1 S.C.R. 12. In
that decision the Supreme Court of Canada commented on the breadth of the
ministerial discretion over the issuance of licences.
[67]
Acknowledging
the discretion over the issuance of licenses, the Applicant submits that this
broad discretion is subject to the purpose of conservation since no minister
has the right to issue licenses that would eliminate a fish habitat. It argues
that since the broad discretion granted by section 7 of the Act is subject to
the principle of conservation, then the regulation-making authority of
subsections 34(2), 36(5) and 38(9) of the Act is likewise to be exercised in a
manner that ensures conservation.
[68]
Further,
it argues that if Parliament intended to authorize the Governor in Council to
enact regulations with such extreme effect as the destruction of a fishery then
it should have clearly granted a wide power such as the one found in section 7.
Since subsections 34(2), 36(5) and 38(9) are narrower than section 7, they
cannot authorize the enactment of the challenged regulations.
[69]
In
my opinion, this argument cannot succeed. In the first place, the Applicant is
mistaken when asserting that conservation is the paramount purpose of the Act.
The Act contains no “purpose” section. A purpose section that was included in
the Act by means of An Act to amend the Fisheries Act, R.S., 1985, c. 35
(1st Supp.) as section 2.1 was subsequently repealed; see An Act
to amend the Fisheries Act, at section 6.
[70]
The
Supreme Court of Canada in Ward recognized the content of the fisheries
power as including conservation and protection of that resource, as well as its
general management. At paragraph 41 in Ward, the Supreme Court
recognized that many interests are engaged in the management of the fisheries,
including industrial interests, as follows:
These cases put beyond doubt that the fisheries power includes not
only conservation and protection, but also the general "regulation"
of the fisheries, including their management and control. They recognize that
"fisheries" under s. 91(12) of the Constitution Act, 1867 refers
to the fisheries as a resource; "a source of national or provincial
wealth" (Robertson, supra, at p. 121); a "common property
resource" to be managed for the good of all Canadians (Comeau's Sea
Foods, supra, at para. 37). The fisheries resource includes the animals
that inhabit the seas. But it also embraces commercial and economic interests,
aboriginal rights and interests, and the public interest in sport and
recreation.
[71]
In
my opinion, the presence or absence of a purpose provision does not impact the
validity of the Act and in any event, no challenge has been made to the vires
of any of the provisions of the Act, only to certain Regulations, that is
section 5, section 27.1 and Schedule 2 of the Regulations.
[72]
The
appropriate analysis in considering the vires of a regulation is that
set out by the Federal Court of Appeal in its decision in Canada (Wheat
Board) v. Canada (Attorney General), [2010] 3 F.C.R. 374 at paragraph 46
where the Court said the following:
The first step in a vires analysis is to identify
the scope and purpose of the statutory authority pursuant to which the impugned
order was made. This requires that subsection 18(1) be considered in the
context of the Act read as a whole. The second step is to ask whether the grant
of statutory authority permits this particular delegated legislation (Jafari
v. Canada (Minister of Employment and Immigration), [1995] 2 F.C. 595
(C.A.), page 602).
[73]
Addressing
the first element, the Act contains many provisions that authorize the
enactment of regulations. Three provisions are referred to in the preamble to
the 2002 Regulations, that is subsections 34(2), 36(5) and 38(9). The preamble
to the 2006 Regulations refers only to subsections 36(5) and 38(9). In my
opinion, subsection 36(5) is the most relevant to the issues raised in this
proceeding and provides as follows:
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36(5) The Governor in Council
may make regulations for the purpose of paragraph (4)(b) prescribing
(a) the deleterious substances
or classes thereof authorized to be deposited notwithstanding subsection (3);
(b) the waters or places or
classes thereof where any deleterious substances or classes thereof referred
to in paragraph (a) are authorized to be deposited;
(c) the works or undertakings
or classes thereof in the course or conduct of which any deleterious
substances or classes thereof referred to in paragraph (a) are authorized to
be deposited;
(d) the quantities or
concentrations of any deleterious substances or classes thereof referred to
in paragraph (a) that are authorized to be deposited;
(e) the conditions or
circumstances under which and the requirements subject to which any
deleterious substances or classes thereof referred to in paragraph (a) or any
quantities or concentrations of those deleterious substances or classes thereof
are authorized to be deposited in any waters or places or classes thereof
referred to in paragraph (b) or in the course or conduct of any works or
undertakings or classes thereof referred to in paragraph (c); and
(f) the persons who may
authorize the deposit of any deleterious substances or classes thereof in the
absence of any other authority, and the conditions or circumstances under
which and requirements subject to which those persons may grant the
authorization.
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36(5) Pour l’application de
l’alinéa (4)b), le gouverneur en conseil peut, par règlement, déterminer :
a) les substances ou catégories
de substances nocives dont l’immersion ou le rejet sont autorisés par
dérogation au paragraphe (3);
b) les eaux et les lieux ou
leurs catégories où l’immersion ou le rejet des substances ou catégories de
substances visées à l’alinéa a) sont autorisés;
c) les ouvrages ou entreprises
ou catégories d’ouvrages ou d’entreprises pour lesquels l’immersion ou le
rejet des substances ou des catégories de substances visées à l’alinéa a)
sont autorisés;
d) les quantités ou les degrés
de concentration des substances ou des catégories de substances visées à
l’alinéa a) dont l’immersion ou le rejet sont autorisés;
e) les conditions, les
quantités, les exigences préalables et les degrés de concentration autorisés
pour l’immersion ou le rejet des substances ou catégories de substances
visées à l’alinéa a) dans les eaux et les lieux visés à l’alinéa b) ou dans
le cadre des ouvrages ou entreprises visés à l’alinéa c);
f) les personnes habilitées à
autoriser l’immersion ou le rejet de substances ou de catégories de
substances nocives en l’absence de toute autre autorité et les conditions et
exigences attachées à l’exercice de ce pouvoir.
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[74]
To determine the
scope and operation of the statutory authority given by subsection 36(5), it is
necessary to read that provision in conjunction with subsection 36(3) and
paragraph 36(4)(b) of the Act, as follow:
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36(3) Subject to subsection (4), no person shall deposit or
permit the deposit of a deleterious substance of any type in water frequented
by fish or in any place under any conditions where the deleterious substance
or any other deleterious substance that results from the deposit of the
deleterious substance may enter any such water.
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36(3) Sous réserve du
paragraphe (4), il est interdit d’immerger ou de rejeter une substance nocive
— ou d’en permettre l’immersion ou le rejet — dans des eaux où vivent des
poissons, ou en quelque autre lieu si le risque existe que la substance ou
toute autre substance nocive provenant de son immersion ou rejet pénètre dans
ces eaux.
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36(4) No person contravenes subsection (3) by
depositing or permitting the deposit in any water or place of
[…]
(b) a deleterious substance of a class and under conditions
— which may include conditions with respect to quantity or concentration —
authorized under regulations made under subsection (5) applicable to that
water or place or to any work or undertaking or class of works or
undertakings; or
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36(4) Par dérogation au
paragraphe (3), il est permis d’immerger ou de rejeter :
[…]
b) les substances nocives
appartenant à une catégorie autorisée sous le régime des règlements
applicables aux eaux ou lieux en cause, ou aux ouvrages ou entreprises ou à
leurs catégories, pris en vertu du paragraphe (5), et ce selon les conditions
— notamment quantités et degrés de concentration — prévues sous leur régime;
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[75]
Subsection
36(3) of the Act prohibits the deposit of a deleterious substance in
fish-bearing waters. Paragraph 36(4)(b) permits the deposit of a deleterious
substance in such waters under conditions authorized by regulations enacted
pursuant to subsection 36(5). The challenged Regulations in this case were
enacted pursuant to subsection 36(5). The effect of the impugned Regulations is
to allow the use of Sandy Pond as a TIA, that is as a depository of residue
generated by the operation of the Project at Long Harbour.
[76]
There
is no doubt that the said residue, that is the tailings, contains deleterious
substances and that these substances will be deposited in Sandy Pond. While
this prospect stirred public opinion and precipitated this litigation, the use
of Sandy Pond in this manner is not illegal but expressly authorized by the
above-referenced provisions of the Act.
[77]
In
my opinion, the provisions quoted above are sufficiently broad to authorize the
enactment of the challenged Regulations, that is the 2006 version.
[78]
The
second step, in the vires analysis, is to inquire whether the grant of
statutory authority permits the delegated legislation in question. In my
opinion it is necessary to focus only on subsection 36(5) in assessing the
second aspect of the vires test per Canada (Wheat Board), because
this provision relates to all three aspects of the Applicant’s challenge, that
is the vires of sections 5 and 27.1, as well as Schedule 2.
[79]
I
will first look at section 5 of the 2006 Regulations which authorizes the
deposit of deleterious materials into a TIA. Section 5 provides as follows:
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5. (1) Despite section 4, the
owner or operator of a mine may deposit or permit the deposit of waste rock
or an effluent that contains any concentration of a deleterious substance and
that is of any pH into a tailings impoundment area that is either
(a) a water or place set out in
Schedule 2; or
(b) a disposal area that is
confined by anthropogenic or natural structures or by both, other than a
disposal area that is, or is part of, a natural water body that is frequented
by fish.
(2) The authority in subsection
(1) is conditional on the owner or operator complying with sections 7 to 28.
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5. (1) Malgré l’article 4, le
propriétaire ou l’exploitant d’une mine peut rejeter — ou permettre que
soient rejetés — des stériles ou un effluent, quel que soit le pH de
l’effluent ou sa concentration en substances nocives, dans l’un ou l’autre
des dépôts de résidus miniers suivants :
a) les eaux et lieux mentionnés
à l’annexe 2;
b) toute aire de décharge
circonscrite par une formation naturelle ou un ouvrage artificiel, ou les
deux, à l’exclusion d’une aire de décharge qui est un plan d’eau naturel où
vivent des poissons ou qui en fait partie.
(2) Le propriétaire ou
l’exploitant ne peut se prévaloir du droit que lui confère le paragraphe (1)
que s’il satisfait aux exigences prévues aux articles 7 à 28.
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[80]
This
conduct is specifically authorized by paragraphs 36(5)(a) to (d) of the Act as
follows:
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36(5) The Governor in Council may make regulations
for the purpose of paragraph (4)(b) prescribing
(a) the deleterious substances or classes thereof
authorized to be deposited notwithstanding subsection (3);
(b) the waters or places or classes thereof where
any deleterious substances or classes thereof referred to in paragraph (a)
are authorized to be deposited;
(c) the works or undertakings or classes thereof
in the course or conduct of which any deleterious substances or classes
thereof referred to in paragraph (a) are authorized to be deposited;
(d) the quantities or concentrations of any
deleterious substances or classes thereof referred to in paragraph (a) that
are authorized to be deposited;
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36(5) Pour l’application de
l’alinéa (4)b), le gouverneur en conseil peut, par règlement, déterminer :
a) les substances ou catégories
de substances nocives dont l’immersion ou le rejet sont autorisés par dérogation
au paragraphe (3);
b) les eaux et les lieux ou
leurs catégories où l’immersion ou le rejet des substances ou catégories de
substances visées à l’alinéa a) sont autorisés;
c) les ouvrages ou entreprises
ou catégories d’ouvrages ou d’entreprises pour lesquels l’immersion ou le
rejet des substances ou des catégories de substances visées à l’alinéa a)
sont autorisés;
d) les quantités ou les degrés
de concentration des substances ou des catégories de substances visées à
l’alinéa a) dont l’immersion ou le rejet sont autorisés;
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[81]
Section
27.1 of the 2006 Regulations requires that a mine owner or operator submit a
compensation plan for approval by the Minister prior to the deposit of
deleterious substances. Section 27.1 reads as follows:
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27.1 (1) The owner or operator of a mine shall
submit to the Minister for approval a compensation plan and obtain the
Minister’s approval of that plan before depositing a deleterious substance
into a tailings impoundment area that is added to Schedule 2 after the coming
into force of this section.
(2) The purpose of the compensation plan is to
offset for the loss of fish habitat resulting from the deposit of a
deleterious substance into the tailings impoundment area.
(3) The compensation plan shall contain the
following elements:
(a) a description of the location of the tailings
impoundment area and the fish habitat affected by the deposit;
(b) a quantitative impact assessment of the
deposit on the fish habitat;
(c) a description of the measures to be taken to
offset the loss of fish habitat caused by the deposit;
(d) a description of the measures to be taken
during the planning and implementation of the compensation plan to mitigate
any potential adverse effect on the fish habitat that could result from the
plan’s implementation;
(e) a description of measures to be taken to
monitor the plan’s implementation;
(f) a description of the measures to be taken to
verify the extent to which the plan’s purpose has been achieved;
(g) a description of the time schedule for the
plan’s implementation, which time schedule shall provide for achievement of
the plan’s purpose within a reasonable time; and
(h) an estimate of the cost of implementing each
element of the plan.
(4) The owner or operator shall submit with the
compensation plan an irrevocable letter of credit to cover the plan’s
implementation costs, which letter of credit shall be payable upon demand on
the declining balance of the implementation costs.
(5) The Minister shall approve the compensation
plan if it meets the requirements of subsections (2) and (3) and the owner or
operator has complied with subsection (4).
(6) The owner or operator shall ensure that the
compensation plan approved by the Minister is implemented.
(7) If the measures referred to in paragraph (3)(f)
reveal that the compensation plan’s purpose is not being achieved, the owner
or operator shall inform the Minister and, as soon as possible in the
circumstances, identify and implement all necessary remedial measures.
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27.1 (1) Le propriétaire ou l’exploitant
d’une mine présente au ministre un plan compensatoire pour approbation et
doit obtenir celle-ci avant de rejeter des substances nocives dans tout dépôt
de résidus miniers qui est ajouté à l’annexe 2 après l’entrée en vigueur du
présent article.
(2) Le plan compensatoire a
pour objectif de contrebalancer la perte d’habitat du poisson consécutive au
rejet de substances nocives dans le dépôt de résidus miniers.
(3) Le plan compensatoire
comporte des dispositions portant sur les éléments suivants :
a) une description de
l’emplacement du dépôt de résidus miniers et de l’habitat du poisson atteint
par le rejet de substances nocives;
b) l’analyse quantitative de
l’incidence du rejet sur l’habitat du poisson;
c) les mesures visant à
contrebalancer la perte d’habitat du poisson;
d) les mesures envisagées
durant la planification et la mise en oeuvre du plan pour atténuer les effets
défavorables sur l’habitat du poisson qui pourraient résulter de la mise en
oeuvre du plan;
e) les mesures de surveillance
de la mise en oeuvre du plan;
f) les mécanismes visant à
établir dans quelle mesure les objectifs du plan ont été atteints;
g) le délai pour la mise en
oeuvre du plan, lequel délai permet l’atteinte des objectifs prévus dans un
délai raisonnable;
h) l’estimation du coût de mise
en oeuvre de chacun des éléments du plan.
(4) Le propriétaire ou
l’exploitant présente, avec le plan compensatoire, une lettre de crédit
irrévocable couvrant les coûts de mise en oeuvre du plan et payable sur
demande à l’égard du coût des éléments du plan qui n’ont pas été mis en
oeuvre.
(5) Le ministre approuve le
plan compensatoire si les exigences des paragraphes (2) et (3) ont été
remplies et si le propriétaire ou l’exploitant s’est conformé aux exigences
du paragraphe (4).
(6) Le propriétaire ou
l’exploitant veille à ce que le plan compensatoire soit mis en oeuvre.
(7) Si les mécanismes visés à
l’alinéa (3)f) révèlent que les objectifs n’ont pas été atteints, le
propriétaire ou l’exploitant en informe le ministre et, le plus tôt possible
dans les circonstances, détermine et prend les mesures correctives
nécessaires à l’atteinte des objectifs.
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[82]
The
compensation plan in this case is reviewed in the affidavits of Mr. McCarthy,
on behalf of the Intervener Vale, and Mr. Barnes on behalf of the Respondent.
[83]
Vale
developed a compensation plan after undertaking an extensive environmental
study of Sandy Pond, following comments from DFO. The plan would relocate the
fish from Sandy Pond to a nearby water source with a minimal loss of life,
including efforts to replace the fish habitat lost through the use of Sandy
Pond as a TIA. The compensation plan was finalized and submitted to DFO in
April 2011.
[84]
The
compensation plan scheme is authorized by paragraph 36(5)(e) of the Act which
provides as follows:
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36(5) The Governor in Council may make regulations
for the purpose of paragraph (4)(b) prescribing
[…]
(e) the conditions or circumstances under which
and the requirements subject to which any deleterious substances or classes thereof
referred to in paragraph (a) or any quantities or concentrations of those
deleterious substances or classes thereof are authorized to be deposited in
any waters or places or classes thereof referred to in paragraph (b) or in
the course or conduct of any works or undertakings or classes thereof
referred to in paragraph (c); and
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36(5) Pour l’application de
l’alinéa (4)b), le gouverneur en conseil peut, par règlement, déterminer :
[…]
e) les conditions, les
quantités, les exigences préalables et les degrés de concentration autorisés
pour l’immersion ou le rejet des substances ou catégories de substances
visées à l’alinéa a) dans les eaux et les lieux visés à l’alinéa b) ou dans
le cadre des ouvrages ou entreprises visés à l’alinéa c);
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[85]
Finally,
there remains the challenge to the creation of Schedule 2 which is a list of
TIAs authorized under the Regulations. The basis of the challenge here is the
alleged invalidity of section 5 of the 2006 Regulations. However, this argument
must fail because section 5 falls within the regulation-making authority of
subsection 36(5). The validity of Schedule 2 depends on the validity of section
5 and I have found section 5 to be valid.
[86]
In
any event, paragraph 36(5)(b) of the Act clearly authorizes the creation of TIAs,
as appears from the following:
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36(5) The Governor in Council may make regulations
for the purpose of paragraph (4)(b) prescribing
[…]
(b) the waters or places or classes thereof where
any deleterious substances or classes thereof referred to in paragraph (a)
are authorized to be deposited;
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36(5) Pour l’application de
l’alinéa (4)b), le gouverneur en conseil peut, par règlement, déterminer :
[…]
b) les eaux et les lieux ou
leurs catégories où l’immersion ou le rejet des substances ou catégories de
substances visées à l’alinéa a) sont autorisés;
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[87]
The
Act authorizes activities that may negatively affect fish-bearing waters, as
recognized by the Court in Ecology Action Centre Society, at paragraph
74 where the Court said the following:
Furthermore,
it is noteworthy that section 35 does not impose a blanket prohibition against
HADD [harmful alteration disruption or destruction of fish habitat]. HADD may
occur with the authorization of the Minister pursuant to regulations enacted by
the Governor-in Council.
[88]
The
fact that regulations enacted pursuant to the Act may have negative
environmental consequences does not, per se, render those regulations
invalid. Parliament legislated the provisions allowing the enactment of the
Regulations in question here. There is no basis for judicial intervention. The
will of the people, with respect to legislation, can be expressed at the ballot
box.
[89]
The
Applicant did not seek injunctive relief to stop any work undertaken in the
conversion of Sandy Pond into a TIA. Accordingly, there was no impediment
against any steps taken by Vale in pursuit of that aim.
[90]
In
the result, I am satisfied that the provisions of the 2006 Regulations that are
challenged in this application were lawfully enacted by the Governor in Council
pursuant to the authority conferred by subsection 36(5) of the Act.
[91]
Two
residual matters require comment, that is the Intervener’s rights to appeal and
costs.
[92]
The
first matter was addressed by the Federal Court of Appeal in its Order of April
8th, 2011 at paragraph 1.(x) as follows:
the
interveners may ask the presiding judge upon the hearing of this application to
entertain a motion for the interveners to have the right to appeal from the
final judgment disposing of the application for judicial review;
[93]
The
Interveners did not raise the issue at the hearing of this matter and the
matter should be raised before the Federal Court of Appeal if necessary.
[94]
The
Order granting status to the Interveners addressed costs at paragraph 1.(xi) as
follows:
the
interveners shall not be entitled to seek costs against the Applicant or the Respondent
nor shall the Applicant or the Respondent be entitled to seek costs against the
interveners whatsoever for the whole of this proceeding.
[95]
In
these circumstances, no costs will be awarded for or against the Interveners.
[96]
In
his submissions the Respondent sought dismissal of this application with costs.
The Respondent has succeeded and in the usual course of events, costs are
awarded to the successful party.
[97]
Accordingly,
this application is dismissed with costs.
JUDGMENT
THIS
COURT’S JUDGMENT is that this
application is dismissed with costs.
“E.
Heneghan”