Endocoal Limited v Glencore Coal Queensland Pty Ltd and Department of Environment and Heritage Protection [2014] QLC 54 (2014) 35 QLCR 462
LAND COURT OF QUEENSLAND
CITATION: Endocoal Limited v Glencore Coal Queensland Pty Ltd
and Department of Environment and Heritage Protection
[2014] QLC 54
PARTIES: Endocoal Limited
(applicant)
v
Glencore Coal Queensland Pty Ltd
(respondent)
and
Chief Executive, Department of Environment and Heritage
Protection
(statutory party)
FILE NOS: MRA711-13
EPA712-13
DIVISION: General Division
PROCEEDING: Application for mining lease and objections; objections to
application for environmental authority, and objections to
conditions included in the draft environmental authority
DELIVERED ON: 16 December 2014
DELIVERED AT: Brisbane
HEARD ON: 21, 22, 23, 25 July 2014
4 December 2014
HEARD AT: Brisbane
MEMBER: PA Smith
ORDERS: 1. I recommend to The Honourable The Minister
responsible for the MRA that MLA 70452 be
granted, subject to the insertion of a special
condition into the Mining Lease that Endocoal
enter into a make good agreement with Glencore,
within either 12 months of the grant of MLA 70452
or before commencement of mining activities,
whichever is the sooner.
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2
2. I recommend to The Honourable The Minister
responsible for the EPA that the amended EA as
set out in Exhibit 25 be granted, subject to
amendments being made consistent with
Attachment 1 to these reasons.
CATCHWORDS: Mining – application for mining lease – objections –
functions and powers of Land Court – statutory criteria in
considering grant – Mineral Resources Act 1989 (MRA) ss
268, 269
Mining – application for environmental authority –
objections – functions and powers of Court –
Environmental Protection Act 1994 (EPA) ss 217, 219,
222, 223
Mining – Mineral Resources Act 1989 and Environmental
Protection Act 1994 – different and competing objects
Mining – application for mining lease – whether some
water issues can fall under MRA and EPA
Mining – application for mining lease – application of
precautionary principle – EPA
Mining – make good agreement – whether applicant and
objector should be ordered to enter into agreement as a
condition of the mining lease
Environmental Authority – whether EA should be
outcome based or prescriptive
Environmental Protection Act 1994
Environmental Protection (Greentape Reduction) and
Other Legislation Amendment Act 2012 No. 16
Mineral Resources Act 1989
Water Act 2000
Water Reform and Other Legislation Amendment Act 2014
Associated Minerals Consolidated Ltd v Wyong Shire
Council (1974) 2 NSWLR 681
Boothey v Boothey (1997) BC9700784
CMR of Police v Eaton (2013) 294 ALR 608
De Lacey & Anor v Kagara Pty Ltd (2009) 30 QLCR 57
Donovan v Struber & Ors (2011) 32 QLCR 226
Hancock Coal Pty Ltd v Kelly & Ors and Department of
Environment and Heritage Protection (No. 4) [2014] QLC
12
Savimaki & Ors v Sunshine Coast Regional Council
[2013] QLC 33
South Australia v Tanner (1988-89) 161 CLR 166
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3
Xstrata Coal Queensland Pty Ltd & Ors v Friends of the
Earth – Brisbane Co-Op Ltd & Ors and Department of
Environment and Resource Management [2012] 33 QLCR
79
APPEARANCES: P Ambrose QC for the applicant
DG Clothier QC with R Anderson for the objector
A Ireland for the statutory party
SOLICITORS: Clayton Utz for the applicants
Allens for the objector
Background
[1] The applicant Endocoal Limited (Endocoal) is proposing to develop an open cut coal
mine, which it has given the name of Meteor Downs South (MDS). To achieve this goal,
Endocoal lodged Mining Lease Application 70452 (MLA 70452) on 29 April 2011. At
the same, time, Endocoal also applied for an environmental authority for MDS. Draft
Environmental Authority EPML00559513 (EA) subsequently issued.1
[2] MLA 70452 is located approximately 30 km south-east of Springsure. Endocoal proposes
the extraction of approximately 1.5 million Run of Mine (ROM) tonnes of low ash export
grade thermal coal per annum.
[3] A term of 15 years is sought for MLA 70452. At the time of the original application,
MLA 70452 covered an area of 1,607 ha. Actual extraction of coal is expected to take
eight to nine years, with the balance of time required for preparatory works and
rehabilitation.
[4] As Mr Ambrose QC for Endocoal has pointed out, in terms of other Central Queensland
coal mines, MDS is not a large operation.
[5] Certificates of Application and Public Notice were issued to Endocoal on 3 October
2013.
[6] Following public notification, Glencore Coal Queensland Pty Ltd (Glencore)2 made
objections to both MLA 70452 and the EA.
[7] In light of the objections lodged, it is the Land Court’s task to hear and determine the
objections to MLA 70452 pursuant to the provisions of the Mineral Resources Act 1989
(MRA), as well as the objections to the EA under the Environmental Protection Act 1994
(EPA), and to then make relevant recommendations to the respective Ministers for each
piece of legislation.
1 The core reference for the information contained in this summary is the Mining Registrar’s report (Exhibit 26) as
well as the submissions of each party.
2 Note that Glencore was previously known as Xstrata Coal Queensland Pty Ltd.
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[8] Glencore’s objections initially related to the inclusion of restricted land in the MLA as
well as impacts on a water supply known as Naroo Dam. Following a change in the
mining program, the issues relating to restricted land are no longer in issue. The central
issue is therefore Naroo Dam.
[9] Glencore operates the Rolleston Coal Mine (RCM) which neighbours the proposed MDS.
RCM is ML 70307.
[10] RCM is a large scale coal mining operation, much larger than the proposed MDS.
Further, Glencore has advanced plans to substantially increase the size of the RCM. It
has already made application for additional mining tenures. MLA 70415 is particularly
relevant in this regard.
[11] Glencore uses Naroo Dam as a source of potable water for its RCM mining operations. It
is concerned that MDS will have a substantial impact on Naroo Dam and therefore on
RCM.
[12] At its highest, Glencore submits that neither MLA 70452 nor the EP should be granted
due to the nature of impacts on RCM.
[13] Alternatively, Glencore seeks a condition that, in the event both MLA 70452 and the EA
are granted, there be a requirement for Endocoal to make good the water Glencore loses
from Naroo Dam because of the MDS mining operation, and also that special conditions
be added to the EA.
[14] Both Endocoal and Glencore have assisted the Court by providing summaries of their
respective positions. The summaries clearly bring the issues in the case into focus.
[15] Endocoal in its summary has this to say:
“2. Summary
Authorisation for Naroo Dam
2.1 Glencore's objections centre around the impacts of mining on MLA 70452 on
Naroo Dam, which Glencore says, and it is accepted as correct by Endocoal, is
used to support its RCM operations that are adjacent to MLA 70452. In
particular, Glencore say that they use Naroo Dam as a potable water source for
the RCM accommodation village (the majority of which is located off the
RCM lease being ML 70307).
2.2 As a threshold issue, there is a serious question as to whether Glencore
currently has the appropriate authorisation to use water from Naroo Dam for
that purpose. For the purpose of these proceedings, Endocoal has proceeded on
the basis that Glencore does have an appropriate authorisation to take water
form Naroo Dam, however this issue must be determined without doubt for the
purposes of implementing any make good condition. That is not a matter for
these proceedings.
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Impacts properly assessed
2.3 Glencore assert that mining on MLA 70452 will have a significant impact on
the surface water and ground water inflows to Naroo Dam, and the quality of
water in Naroo Dam. Glencore also assert that such impacts have not been
properly assessed, and are too uncertain for the grant of MLA 70452 to be
recommended by the Court. It is clear that what Glencore really seeks to know
is what are, in each year of operation, the measured impacts of the operation.
This is obviously unreasonable. The information of, for example, the sediment
runoff in year 5 of operations, is not possible to know in advance of year 5. In
any case, that figure is not the impact on Naroo Dam. The impact is sediment
runoff, and the degree of impact is capable of measurement within the proper
bounds of scientific modelling (for example by using likely rainfall).
2.4 It is proper to acknowledge that the likely impacts are, for example, quantity
and quality of runoff into the receiving environment (generally not only in
relation to one part of that receiving environment) and, as is conventional, to
model the worst and likely scenarios and describe the measures to mitigate
those impacts. This is precisely what Endocoal's experts have done.
2.5 Glencore are seeking to require Endocoal to collect further long term data prior
to mining, however, Endocoal's position is that there is already an important set
of existing data in relation to Naroo Dam, and ultimately it is the quality (rather
than quantity) of data that is important. The project on MLA 70452 involves a
relatively a small system that can be studied intensely over a short period of
time, where the new data can be informed by the existing long-term dataset.
Endocoal's position is that new data can be collated during mining in
accordance with the recommendations of the experts.1 [(1) Refer to transcript of
proceedings on 22 July 2014, page 2-55, lines 15 to 35, evidence of Mr Roads, where
he states that Endocoal does not need any more data to identify the extent of the
impacts of surface water issues prior to mining commencing. Also refer to Exhibit 6 -
Joint Expert Report to the Land Court by Dr Noel Merrick and Mr John Bradley,
paragraph 2.6(f) and (g) and Exhibit 24 - Further statement of evidence of John
Bradley dated 18 July section 2(a). Both experts agree that trigger levels be set after 12
months of data has been collected, but that it is only necessary to collect 6 months of
data before commencement of excavation below the water table, provided that bores
are installed and monitoring commences prior to the next wet season. Mr Scott and Mr
Tarlinton make similar statements about data being collected following the grant of the
mining lease (Transcript of proceedings on 23 July 2014, page 3-66, lines 1 to 15,
evidence of Mr Scott, and page 3-62, lines 30 to 45).]
Extreme positions taken by Glencore
2.6 Glencore's witnesses have consistently adopted extreme positions as to:
(a) the level of importance that Glencore and the RCM places on Naroo Dam
as a water supply; and
(b) the impacts mining on MLA 70452 will have on Naroo Dam, in an effort to
persuade the Court that MLA 70452 should not be granted. Glencore's
experts say that mining on MLA 70452 will have catastrophic
consequences for Glencore and the State of Queensland. However, the
evidence has shown that the importance of Naroo Dam as a water supply to
the RCM has been greatly overstated by Glencore (particularly given that
Glencore does have viable alternative supplies of water), and that the
extreme positions about the potential impacts of mining on MLA 70452 are
highly unlikely to occur.
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Adoption of expert recommendations and make good commitment
2.7 Despite Glencore's assertions, the ground water and surface water experts have
largely agreed as to the possible extent of the impacts, with only some
disagreement about worst case scenarios which the experts agree are unlikely
to occur. These, and other experts (particularly in relation to rehabilitation
including erosion and sediment control), have made certain recommendations
to ensure that the actual impacts are assessed and minimised during mining
operations.
2.8 Certain recommendations by Glencore's experts relating to rehabilitation seek
to persuade the Court or DEHP to return to a prescriptive regime rather than
one which is currently adopted and which is outcome based.2 [Transcript of
proceedings on 23 July 2014, evidence of Mr Tarlinton, page 3-61, lines 25 to 45
where DEHP’s current position is outlined.] The EA conditions are designed to
prescribe outcomes to be achieved to avoid general environment harm.
Particular impacts upon an individual person/company, in this case Glencore,
are properly dealt with by a specific make good condition, not general EA
conditions designed to protect various environmental values.
2.9 Endocoal is committed to implementing many of the practical
recommendations made by the relevant experts including through
implementation of the various plans and management strategies required in the
draft EA.
2.10 Although, based on the evidence, there are very good arguments that no make
good condition is required in this case including because:
(a) Glencore may not have a current or future entitlement to the water;
(b) Glencore's evidence is very unclear as to past, current and future uses of
the water (which makes it difficult to design any make good condition
unless in the most general of terms);
(c) the dam is likely to run out of water without mining on MLA 70452
occurring;
(d) Glencore clearly have alternate supplies of water; and
(e) arguably impacts on water are more appropriately dealt with under the
Water Act 2000 (Qld) as submitted by DEHP,
if the Court is minded to impose such a condition, Endocoal has indicated its
willingness to make good any impacts caused by such mining on the quantity
and quality of water in Naroo Dam, which Glencore would otherwise be
entitled to take had operations on MLA 70452 not occurred. Given that
Endocoal agrees to make good impacts, it is in Endocoal's interests to ensure
that such impacts are minimised.
2.11 Glencore suggest that Endocoal may not have the ability to make good such
impacts, but there are a long line of authorities that require an assumption to be
made that a ML/EA holder will comply with the conditions of those
authorities.
No good reason for refusal of MLA 70452 and EA
2.12 Endocoal submits that it has met the requirements of the MRA and EP Act with
respect to the grant of MLA 70452 and the EA.3 [Exhibit 1 – Affidavit of Darren
Noel Walker Sworn 12 March 2014, paragraphs 21 to 75. Also refer to paragraph 5
regarding the applicability of the Environmental Protection (Greentape Reduction) Act
2012 (Qld) to the EA application.]
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2.13 DEHP also considers that the EA adequately protects the relevant
environmental values, and that the EA conditions are appropriate.
2.14 In the above circumstances, in Endocoal's submission, there is no good reason
for MLA 70452 and the EA not to be granted.
[16] Glencore’s summary is as follows:
“SUMMARY
1. The circumstances of this proceeding are unique.
2. The applicant (Endocoal) proposes to develop and operate an open cut coal mine
to be known as Meteor Downs South (MDS). Should it proceed, MDS will be in
close proximity to Naroo Dam which, since October 2012, has been known by
Endocoal to be the source of raw water for potable supply in connection with a
neighbouring and much larger mine, the Rolleston Coal Mine (RCM)1 [Ex 22
para 38]. Endocoal has designed MDS such that water from spoil dumps and
industrial areas will drain into Naroo Dam. In the experience of Mr Scott, a
geochemist with over 42 years experience in relation to coal mines, that is
unprecedented2 [As identified below, Mr Walker’s experience is to the same effect. No
other witness suggested anything that contradicted Mr Scott’s experience.]
3. It is clear on the expert evidence before the Court that MDS will have adverse
impacts on Naroo Dam. The areas of controversy in relation to that evidence
relate principally to the extent of the impacts. On the evidence before the Court,
those areas of controversy exist only because Endocoal has not done the work to
determine the impacts with reasonable certainty. Principally, it has not collected
adequate data in relation to stream flow in the Naroo Dam catchment, water
quality in relation to that stream flow or Naroo Dam or soil or overburden
characteristics. There is no explanation (or excuse) for this.
4. In the submission of the respondent (Glencore), these are good reasons why the
Court should recommend against both MLA 70452 and the draft Environmental
Authority (EA). Whether or not this may delay MDS3 [There is no real evidence of
this. Endocoal has said that it intends to commence the construction of MDS as soon as a
mining lease is granted: ex 1, para 29. It even told the Commonwealth in May 2014 that
the initial stage of construction was expected to commence in mid 2014 even though the
trial of this proceeding had been set down for July 2014 and therefore no
recommendation had been made by the Court: ex 27, section 2.6.1.1 (p.29). Endocoal has
also said that its parent company (U&D Coal Ltd) has the necessary funding to establish
MDS: ex 1, para 38. But the statement of technical and financial capabilities was
deliberately omitted from ex 1 and there is no supporting evidence for this statement. The
evidence suggests that detailed planning is on hold pending the grant of a mining lease
and, moreover, that U&D Coal Ltd is in dispute with its major shareholder over whether
a capital contribution of approximately $50m must be refunded]
5. If the Court were minded to recommend in favour of the MLA and draft EA, it
should also recommend stringent conditions. It is not to the point that goal based
conditions may currently be in vogue within the Department. The Court is not
bound by the approach of the Department. The very reason this process exists is
to provide independent oversight over MLAs and draft EAs. There is no
inconsistency between stringent conditions and the relevant goals in this case as
stringent conditions can only assist the achievement of those goals. In any event,
an appropriate response to the unique circumstances of this case does not set a
precedent against which other cases will likely be judged.
6. In considering these matters, it is necessary to bear in mind the manner in which
this proceeding comes to the Court.
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7. Inexplicably, in support of its application for an EA, Endocoal caused to be
prepared, and then provided to the Department as the basis for its assessment, an
environmental management plan (EMP)4 [The EMP is ex DNW8 to ex 1. The EMP
includes a Surface Water Assessment Report from WRM (Mr Roads) dated May 2013
(Appendix A), a Baseline Groundwater Study from Coffey Environments dated 21
December 2012 (Appendix B) and a Soils and Overburden Assessment Report from GSS
Environmental dated March 2013] that did not recognise Naroo Dam for its most
important purpose. This is because Endocoal did not tell its consultants about its
most important purpose5 [Mr Roads agreed it was a material thing to be told and said
he was unaware of it until after objections were lodged (T2‐43/15). The objections are
dated 28 November 2013: exs 10 & 11.]
8. The EMP was prepared by reference to a very different initial development plan
(IDP) that plainly involved significant impacts on Naroo Dam6 [These included the
loss of approximately 87% of the catchment for Naroo Dam, the draining of mine
affected water into Naroo Dam and the mining of part of Naroo Dam. Mr Walker
suggested these matters may not have a significant impact on Naroo Dam. The fact that
Endocoal has changed its IDP as it has demonstrates the lack of merit to that suggestion].
The IDP that Endocoal now relies on7 [Ex DNW19 to ex 1] was only provided in
Endocoal’s material in this proceeding and, to the extent the impacts of it have
been assessed, that has only occurred in this proceeding. The assessment has not
involved the preparation of any revised EMP, the assessment of the proposed
amended EA8 [Ex 25. Mr Tarlinton was asked in cross‐examination whether the
department had any concerns about ex 25. He rightly responded that it would need to be
assessed] by Mr Tarlinton or, apparently, the submission of the IDP under the
Mineral Resources Act 1989 (MRA). What is has involved is the use of the
Court’s processes (including the use of Glencore’s experts) to attempt to do what
should have been done long ago.
9. By reason of the changed IDP, some of Glencore’s objections (and particulars of
objections) are no longer relevant. Examples include objections in relation to the
inclusion of restricted land in the MLA, the mining of restricted land and in
relation to inhibiting access to Naroo Dam. However, Glencore’s objection that
the MLA will have adverse impacts on the quality and quantity of water in Naroo
Dam remain valid.”
[17] Although the statutory party did not provide a summary of its submissions, this was
because its submissions3 were relatively short. The following extracts explain the
position of the statutory party:
“Applicant’s mining proposal
5. The applicant’s application dated 29 April 2011 and environmental management plan
dated 3 May 2013 were received and assessed by the Department of Environment and
Heritage Protection (‘the Department’). That assessment is set out in the Affidavit of
Samuel Edward Tarlinton (exhibit 23) and further detailed in the Department’s
assessment report (exhibit 36).
6. Following assessment in compliance with the Environmental Protection Act 1994 (‘EP
Act’), the Department issued a draft EA on 29 July 2013. The position of the Statutory
Party is that the conditions proposed in the draft EA were reasonable, necessary and
desirable to deal with the impact of the mining activities as provided for in the
applicant’s application documents.
3 Those as amended as at 31 July 2014.
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7. As detailed in paragraphs 77-88 of exhibit 1, the applicant has proposed changes to its
project which are reflected in a revised Initial Development Plan (IDP) and mine water
management system. Those changes are subsequent to the issuing of the draft EA2.
8. The applicant tendered a marked up version of the draft EA (‘the marked up EA’)
(exhibit 25) in the proceedings. The applicant contends that the marked up EA
accommodates the changes to its project.
9. It is important to note that the changes in the marked up EA are not substantive. They
consist of amendment to the approved plans and schedules 2 and 3 to reflect changes in
the location of infrastructure rather than changes to any content requirements of
conditions in the draft EA.2 [The department considers that the changes constitute a minor
change and therefore a new application is not required]
10. In consideration of the changes detailed in paragraph 7 and the evidence in the
proceedings, the department has reviewed the marked up EA. For the reasons outlined
below, the Statutory Party considers that the marked up EA is appropriate and that no
more (or less) stringent conditions are necessary. Accordingly, the Statutory Party
submits that the Court should recommend to the Minister that the marked up EA be
issued.
Impacts to Naroo Dam - interaction between the EP Act and the Water Act 2000
…
14. The Statutory Party submits that the Court can be satisfied that impacts, being, changes
to the yield of water from MLA70452 resulting from the any take of and/or interference
with water caused by the Applicant’s proposal can be effectively dealt with:
a. by the monitoring requirements imposed in the marked up EA (which do not
differ from the draft EA originally issued);
b. the water licence process that the Applicant must go through (including
possible appeal/s to this Court) in respect of groundwater inflows to the mining
pits; and
c. by the current water legislative framework3 [The interference and take of overland
flow water is permissible under section 20(1)(g) of the Water Act 2000 and section
110(2)(d) of the Water Resource (Fitzroy Basin) Plan 2011. As per section 110(1) of
the Water Resource (Fitzroy Basin) Plan 2011, section 110 limits overland flow water
that may be taken under section 20(2)(b) of the Water Act 2000. Therefore, the Water
Act 2000 and subordinate legislation has specifically considered and provided
authorisation for the take and interference of overland flow associated with mining
activities in the Fitzroy Basin] in respect of the take and interference of overland
flow.
Water Quality
…
17. The Statutory Party submits that the impacts on water quality can be effectively dealt
with by the water quality limits included in the marked up EA.
Rehabilitation
18. Evidence was adduced in these proceedings in respect of the adequacy of rehabilitation
conditions, specifically the requirements in the marked up EA pertaining to slopes of
the rehabilitated landform.
…
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20. In respect of both slope and longitudinal drainage gradient, Mr Tarlinton gave oral
evidence that:
a. based on his departmental and personal experience 12 degrees and 2% can be
achieved;
b. 12 degrees and 2% are at upper ends of the spectrum, in other words they are a
maximum reference point; and
c. the Department is concerned with the rehabilitation outcome which is
consistent with the Department’s current practice of imposing outcome based
conditions – in that respect the relevant outcome is the achievement of a stable
landform.
21. Therefore, the applicant must rehabilitate to a stable landform regardless of the
specified maximum slopes. Accordingly, the Statutory Party submits that the
rehabilitation conditions as contained in the marked up EA are achievable and
appropriate.
Sufficiency of data
…
23. The position of the Statutory Party is that there was sufficient information provided in
the application and the environmental management plan to assess the application and
issue a draft EA.
24. Further, there are conditions in the marked EA (which do not differ from the draft EA
originally issued) which require further and ongoing monitoring.
Conclusion
25. The Statutory Party respectfully submits that the Court should recommend to the
Minister that the marked up EA be issued because:
a. the applicant’s application was properly assessed in accordance with theEP Act;
and
b. conditions were included in the draft EA and relevantly, those conditions
remain in the marked up EA, that are necessary and desirable and that
appropriately deal with the impacts that will be caused by the Applicant’s
proposal.
[18] It is often said that a picture is worth a thousand words. Certainly, in this case, a diagram
showing the location of Naroo Dam in relation to the respective mining tenements is
particularly helpful. I thank the parties for providing the following to the Court:
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The Hearing
[19] Both the MRA and EPA matters were heard together. Evidence in one matter was taken
to be evidence in the other matter.
[20] It should also be noted that the statutory party was only a party to the EPA proceedings.
[21] Oral evidence was heard from 21-23 July 2014, and oral submissions were heard on
25 July 2014. The parties also provided written submissions, and further submissions to
take into account further submissions by the statutory party regarding the operation of
legislation relating to water. The further submissions by Endocoal and Glencore were
extensive.
[22] The hearing resumed on 4 December 2014 so that the parties could make further
submissions on the impact of the Water Reform and Other Legislation Amendment Act
2014 (Water Reform Act).
[23] As at 4 December 2014 the Water Reform Act had been passed by Parliament4 but had
not been proclaimed into force. As at the date of delivery of these recommendations, the
Water Reform Act has commenced in part, but those parts impacting on mining tenures
and water have not commenced.
[24] Endocoal was represented throughout the hearing by Mr Ambrose QC, instructed by
Clayton Utz.
[25] Glencore was represented by Mr Clothier QC and Mr Anderson, instructed by Allens.
[26] The statutory party was represented by Ms Ireland, a legal officer with the Department of
Environment and Heritage Protection.
[27] Oral evidence was given during the hearing by the following:
Darren Noel Walker, General Manager, Resource Development, U & D Mining
Industry (Australia) Pty Ltd, called by Endocoal;
Gregory Kenneth Roads, Civil Engineer, WRM Water and Environment Pty Ltd,
called by Endocoal;
John William Bradley, Principal Hydrogeologist, JBT Consulting Pty Ltd, called
by Endocoal;
Rodney Peter Masters, Technical Discipline Executive (Land Assessment
Rehabilitation and closure, water and land engineering, computer aided design and
geographic information systems), SLR Consulting Australia Pty Ltd, called by
Endocoal;
Lindsay Grant Ford, Mining Engineer, Glencore, called by Glencore;
4 On 26 November 2014.
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Stephen John Downes, Water Infrastructure Manager, Glencore, called by
Glencore;
Kenneth John Dixon, Environment and Community Manager, Glencore, called by
Glencore;
Dr Noel Patrick Merrick, Hydrogeologist, HydroAlgorithmics, called by
Glencore;
Anthony Marszalek, Civil Engineer, Gilbert & Associates Pty Ltd, called by
Glencore;
Terrence Andrew Short, Agricultural Scientist, La Tierra Pty Ltd, called by
Glencore;
Samuel Edward Tarlington, Manager of Mining, Mackay, Department of
Environment and Heritage Protection, called by the statutory party
Peter Alexander Scott, Senior Principal Geochemist, O’Kane Consultants Pty Ltd,
called by Glencore.
[28] In making these recommendations, I have taken into account all of the evidence
presented in this case, and have considered and taken into account all of the submissions
of each party. These recommendations refer to the salient points, but not all of the
material, which I have considered.
The statutory framework
[29] In considering many MRA and EPA objections in the past, I have considered in great
detail the relevant legislation. Although what follows is largely taken from Hancock Coal
Pty Ltd v Kelly & Ors and Department of Environment and Heritage Protection (No. 4),5
it is appropriate to again refer to the legislation in detail.
[30] There is a rather complex statutory framework underpinning these matters, which
involves the MRA, the EPA and the Water Act 2000 (Water Act).
[31] As Endocoal’s MLA 70452 is made pursuant to the MRA, it is appropriate to consider
that legislation first.
MRA
[32] Pursuant to s 268 of the MRA, the Court is required to conduct a hearing into the
application for the grant of the mining lease and the MRA objections. Section 268
relevantly provides as follows:
“268 Hearing of application for grant of mining lease
(1) On the date fixed for the hearing of the application for the grant of the
mining lease and objections thereto, the Land Court shall hear the
application and objections thereto and all other matters that pursuant to this
5 [2014] QLC 12.
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part are to be heard, considered or determined by the Land Court in respect
of that application at the one hearing of the Land Court.
(2) At a hearing pursuant to subsection (1) the Land Court shall take such
evidence, shall hear such persons and inform itself in such manner as it
considers appropriate in order to determine the relative merits of the
application, objections and other matters and shall not be bound by any
rule or practice as to evidence.
(3) The Land Court shall not entertain an objection to an application or any
ground thereof or any evidence in relation to any ground if the objection or
ground is not contained in an objection that has been duly lodged in respect
of the application. …”
[33] Section 269 of the MRA then goes on to relevantly provide:
“269 Land Court’s recommendation on hearing
(1) Upon the hearing by the Land Court under this part of all matters in respect
of an application for the grant of a mining lease, the Land Court shall
forward to the Minister—
(a) any objections lodged in relation thereto; and
(b) the evidence adduced at the hearing; and
(c) any exhibits; and
(d) the Land Court’s recommendation.
Note—
For other relevant provisions about forwarding documents, see section
386O.
(2) For subsection (1)(d), the Land Court’s recommendation must consist of—
(a) a recommendation to the Minister that the application be granted or
rejected in whole or in part; and
(b) if the application relates to land that is the surface of a reserve and the
owner of the reserve has not consented to the grant of a mining lease
over the surface area, the following—
(i) a recommendation to the Minister as to whether the Governor in
Council should consent to the grant over the surface area;
(ii) any conditions to which the mining lease should be subject.
(3) A recommendation may include a recommendation that the mining lease be
granted subject to such conditions as the Land Court considers appropriate,
including a condition that mining shall not be carried on above a specified
depth below specified surface area of the land.
(4) The Land Court, when making a recommendation to the Minister that an
application for a mining lease be granted in whole or in part, shall take into
account and consider whether—
(a) the provisions of this Act have been complied with; and
(b) the area of land applied for is mineralised or the other purposes for
which the lease is sought are appropriate; and
(c) if the land applied for is mineralised, there will be an acceptable level
of development and utilisation of the mineral resources within the area
applied for; and
(d) the land and the surface area of the land in respect of which the mining
lease is sought is of an appropriate size and shape in relation to—
(i) the matters mentioned in paragraphs (b) and (c); and
(ii) the type and location of the activities proposed to be carried out
under the lease and their likely impact on the surface of the land;
and
(e) the term sought is appropriate; and
(f) the applicant has the necessary financial and technical capabilities to
carry on mining operations under the proposed mining lease; and
(g) the past performance of the applicant has been satisfactory; and
(h) any disadvantage may result to the rights of—
-- 14 of 60 --
15
(i) holders of existing exploration permits or mineral development
licences; or
(ii) existing applicants for exploration permits or mineral development
licences; and
(i) the operations to be carried on under the authority of the proposed
mining lease will conform with sound land use management; and
(j) there will be any adverse environmental impact caused by those
operations and, if so, the extent thereof; and
(k) the public right and interest will be prejudiced; and
(l) any good reason has been shown for a refusal to grant the mining lease;
and
(m) taking into consideration the current and prospective uses of that land,
the proposed mining operation is an appropriate land use.
(5) Where the Land Court recommends to the Minister that an application for
the grant of a mining lease be rejected in whole or in part the Land Court
shall furnish the Minister with the Land Court’s reasons for that
recommendation.”
[34] The objects of the MRA are also relevant. They are set out in s 2 as follows:
“2 Objectives of Act
The principal objectives of this Act are to—
(a) encourage and facilitate prospecting and exploring for and mining of
minerals;
(b) enhance knowledge of the mineral resources of the State;
(c) minimise land use conflict with respect to prospecting, exploring and
mining;
(d) encourage environmental responsibility in prospecting, exploring and
mining;
(e) ensure an appropriate financial return to the State from mining;
(f) provide an administrative framework to expedite and regulate
prospecting and exploring for and mining of minerals;
(g) encourage responsible land care management in prospecting, exploring
and mining.”
EPA
[35] It should be noted at the outset that the EPA has undergone significant amendment, and
that those amendments directly relate to the objection process under the EPA. The
significant amendments commenced on 31 March 2013.6 For the purposes of this
decision, s 683 of the EPA (as currently enacted) provides that the previous provisions of
the EPA, under former Chapter 5, apply. Accordingly, the provisions which relevantly
commenced on 31 March 2013 are to be ignored. All further references in this decision to
the EPA will be to those provisions from the former Chapter 5 of the EPA.
[36] The object of the EPA is important. Section 3 of the EPA provides as follows:
“3 Object
The object of this Act is to protect Queensland’s environment while
allowing for development that improves the total quality of life, both now
and in the future, in a way that maintains the ecological processes on which
life depends (ecologically sustainable development).
6 See Environmental Protection (Greentape Reduction) and Other Legislation Amendment Act 2012 No. 16.
-- 15 of 60 --
16
4 How object of Act is to be achieved
(1) The protection of Queensland’s environment is to be achieved by an
integrated management program that is consistent with ecologically
sustainable development.
(2) The program is cyclical and involves the following phases—
(a) phase 1—establishing the state of the environment and defining
environmental objectives;
(b) phase 2—developing effective environmental strategies;
(c) phase 3—implementing environmental strategies and integrating them
into efficient resource management;
(d) phase 4—ensuring accountability of environmental strategies.
(3) The relationship between each of the phases is shown in the figure
appearing at the end of this Act.
(4) Phase 1 is achieved by—
(a) researching the state of the environment, including essential ecological
processes; and
(b) deciding environmental values to be protected or achieved by
consulting industry, government departments and the community.
(5) Phase 2 is achieved by—
(a) developing environmental protection policies that, among other
things—
(i) decide environmental indicators; and
(ii) establish ambient and emission standards for contaminants; and
(iii) require waste management, including waste prevention and
minimisation; and
(iv) advise on management practices; and
(b) promoting environmental responsibility and involvement within the
community.
(6) Phase 3 is achieved by—
(a) integrating environmental values into land use planning and
management of natural resources; and
(b) ensuring all reasonable and practicable measures are taken to protect
environmental values from all sources of environmental harm; and
(c) monitoring the impact of the release of contaminants into the
environment; and
(d) requiring persons who cause environmental harm to pay costs and
penalties for the harm.
(7) Phase 4 is achieved by—
(a) reviewing the results of human activities on the environment; and
(b) evaluating the efficiency and effectiveness of environmental strategies;
and
(c) reporting publicly on the state of the environment.
5 Obligations of persons to achieve object of Act
If, under this Act, a function or power is conferred on a person, the person
must perform the function or exercise the power in the way that best
achieves the object of this Act.
6 Community involvement in administration of Act
This Act is to be administered, as far as practicable, in consultation with,
and having regard to the views and interests of, industry, Aborigines and
Torres Strait Islanders under Aboriginal tradition and Island custom,
interested groups and persons and the community generally.”
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17
[37] As I said in the Land Court decision of Donovan v Struber & Ors:7
“[14] The objects of the EP Act are vastly different from the objects of the MRA.
While the key object of the MRA is to facilitate the mining of the State’s
resources, s.3 of the EP Act states that the object of that Act is to protect
Queensland’s environment while allowing for development that improves the
total quality of life, both now and in the future, in a way that maintains the
ecological processes on which life depends (ecologically sustainable
development).
[15] Section 4 of the EP Act provides for an integrated management program,
which involves implementing environmental strategies and integrating them
into efficient resource management. Accountability is an important element,
while s.8 defines ‘environment’ and s.9 defines ‘environmental value’.
Section 14 defines ‘environmental harm’ and how it may be caused by an
activity. Section 15 defines ‘environmental nuisance’ as unreasonable
interference or likely interference with an environmental value caused by:
(a) noise, dust, odour, light; or
(b) an unhealthy, offensive or unsightly condition because of
contamination; or
(c) another way prescribed by regulation”
[38] Section 14 of the EPA refers to environmental harm:
“14 Environmental harm
(1) Environmental harm is any adverse effect, or potential adverse effect
(whether temporary or permanent and of whatever magnitude, duration or
frequency) on an environmental value, and includes environmental
nuisance.
(2) Environmental harm may be caused by an activity—
(a) whether the harm is a direct or indirect result of the activity; or
(b) whether the harm results from the activity alone or from the combined
effects of the activity and other activities or factors.”
[39] The right to make an objection under the EPA is set out in s 216. The objection may be
about the EA Application, the draft EA for the application, or a condition included in the
draft. Glencore did not object about the draft EA for the application.
[40] The decision that this Court makes in hearing the EPA objection is governed by s 222,
which relevantly provides as follows:
“222 Nature of objections decision
(1) The objections decision for the application must be a recommendation to
the EPA Minister that—
(a) the application be granted on the basis of the draft environmental
authority for the application; or
(b) the application be granted, but on stated conditions that are different to
the conditions in the draft; or
(c) the application be refused.
(2) However, if a relevant mining lease is, or is included in, a significant
project and, under section 210, Coordinator-General’s conditions were
included in the draft, any stated conditions under subsection (1)(b)—
(a) must include the Coordinator-General’s conditions; and
(b) must not be inconsistent with a Coordinator-General’s condition.
…”
7 (2011) 32 QLCR 226.
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18
[41] Another important section to be considered by this Court is s 223 of the EPA. That
section provides:
“223 Matters to be considered for objections decision
In making the objections decision for the application, the Land Court must
consider the following—
(a) the application documents for the application;
(b) any relevant regulatory requirement;
(c) the standard criteria;
(d) … ;
(e) each current objection;
(f) any suitability report obtained for the application;
(g) the status of any application under the Mineral Resources Act for each
relevant mining tenement.”
[42] It is via the mechanism of s 223 that the “precautionary principle” comes into play. As I
stated in De Lacey & Anor v Kagara Pty Ltd:8
“[174] ‘Standard criteria’ (see s. 223(c) above) is defined in Schedule 3 of the EP
Act in part as follows:
‘ “standard criteria” means–
the principles of ecologically sustainable development as set out in the
‘National Strategy for Ecologically Sustainable Development’; and . ..
. .’
[175] Further in Schedule 3 of the EP Act, “National Strategy for Ecologically
Sustainable Development” is defined as follows:
‘ “National Strategy for Ecologically Sustainable Development” means
the ‘National Strategy for Ecologically Sustainable Development’
endorsed by the Council of Australian Governments on 7 December
1992.” ’
[176] The National Strategy for Ecologically Sustainable Development of
December 1992 contains the following statement of Australia’s goal, core
objectives and guiding principles for the Strategy:
‘The Goal is:
Development that improves the total quality of life, both now and in
the future, in a way that maintains the ecological processes on which
life depends.
The Core Objectives are:
• to enhance individual and community well-being and welfare by
following a path of economic development that safeguards the
welfare of future generations
• to provide for equity within and between generations
• to protect biological diversity and maintain essential ecological
processes and life-support systems
The Guiding Principles are:
• decision making processes should effectively integrate both long
and short-term economic, environmental, social and equity
considerations
• where there are threats of serious or irreversible environmental
damage, lack of full scientific certainty should not be used as a
8 (2009) 30 QLCR 57. Note paragraphs incorrectly numbered in The Reports as [172] – [176].
-- 18 of 60 --
19
reason for postponing measures to prevent environmental
degradation
• the global dimension of environmental impacts of actions and
policies should be recognised and considered
• the need to develop a strong, growing and diversified economy
which can enhance the capacity for environmental protection
should be recognised
• the need to maintain and enhance international competitiveness in
an environmentally sound manner should be recognised
• cost effective and flexible policy instruments should be adopted,
such as improved valuation, pricing and incentive mechanisms
• decisions and actions should provide for broad community
involvement on issues which affect them
These guiding principles and core objectives need to be considered as a
package. No objective or principle should predominate over the others. A
balanced approach is required that takes into account all these objectives
and principles to pursue the goal of ESD.’
[177] From the precautionary principle perspective, the key is the second bullet
point to the guiding principles in the paragraph above, which sets out in a
lengthened form what is currently referred to as the precautionary principle
– that is, ‘where there are threats of serious or irreversible environmental
damage, lack of full scientific certainty should not be used as a reason for
postponing measures to prevent environmental degradation.’”
Water Act 2000
[43] Depending upon the manner in which any interaction between the Water Act and the
MRA and EPA is viewed, consideration of water issues is either irrelevant to the present
proceedings (the view essentially expressed by Endocoal and the statutory party) or is
fundamental to the proceedings and a matter which can properly be addressed in the
current proceedings (the view expressed by Glencore).
[44] This issue was the subject of significant parts of the reasons in President MacDonald’s
decision in Xstrata Coal Queensland Pty Ltd & Ors v Friends of the Earth – Brisbane
Co-Op Ltd & Ors, and Department of Environment and Resource Management,9 as well
as my decision in Hancock.
[45] Following amendment of the statutory party’s submissions in this matter, this issue has
also become subject to lengthy submissions by Endocoal and Glencore.
[46] The further submissions by Endocoal are well researched and detailed. They seek to
persuade me to come to a different conclusion to what I did in Hancock and to what
President MacDonald found in Xstrata.
[47] In the interests of keeping some sort of control over the final number of paragraphs in
this decision, I will not delve into the details of Endocoal’s submissions on the Water
Act. Suffice it to say that I am not convinced that I should change from my position in
Hancock.
9 (2012) 33 QLCR 79.
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20
[48] In fact, I find myself in the position of agreeing with the summary of Hancock in this
regard set out by Glencore in its submissions of 12 August 2014, as well as Glencore’s
other comments in those submissions relating to the interaction of these matters with the
Water Act. I expressly adopt Glencore’s submissions of 12 August 2014, paragraphs 1–
55, into these reasons, and set them out in the following paragraphs.
Summary regarding Water Act issue
[49] On 31 July 2014, the statutory party filed an Amended Outline of Submissions. The
statutory party’s amended outline contains minor changes to its submissions to the effect
that impacts relating to the “take of water by other users … are matters that sit outside
the EPA Act”, are instead “matters which would be considered in the assessment of an
application for a water licence under the Water Act 2000” and are matters that “can
effectively be dealt with” under (amongst other things) the Water Act 2000.10 The
statutory party’s amended outline does not go substantially beyond what it has already
submitted to the Court.
[50] In purported reply to the statutory party’s amended outline, Endocoal has filed 7 pages of
submissions and provided 34 pages of annexures. Endocoal’s submissions are not
submissions in reply to the minor amendments contained in the statutory party’s
amended outline. They are further submissions that, for example, contend for the first
time that this Court cannot consider issues relating to taking or interfering with water
under the Mineral Resources Act 1989 (MRA) or impose conditions relating to those
matters. The further submissions represent an attempt by Endocoal to fundamentally
change its position in relation to such matters.
[51] The Court does not accept Endocoal’s further submissions.
[52] First, they are not in reply to minor amendments contained in the statutory party’s
amended outline and represent a fundamental change of position by Endocoal. To do
otherwise is to permit Endocoal to reopen its case without any application being made for
it to do so.
[53] Secondly, even if I were minded to embark upon the merits of Endocoal’s further
submissions, the submissions contained in them are flawed and no good reason is
advanced as to why I should not follow the previous decisions in Xstrata11 and
Hancock.12
10 Statutory Party’s Amended Outline, paras 11-14.
11 Xstrata Coal Queensland Pty Ltd & Ors v Friends of the Earth – Brisbane Co-Op Ltd & Ors and Department of
Environment and Resource Management [2012] 33 QLCR 79.
12 Hancock Coal Pty Ltd v Kelly & Ors and Department of Environment and Heritage Protection (No. 4) [2014]
QLC 12.
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21
Endocoal’s Further Submissions are not Reply Submissions
[54] In its original outline, the statutory party appropriately confined itself to submissions in
relation to the draft EA and the Environmental Protection Act 1994 (EP Act), noting that
it is not a party to the MRA proceeding.13
[55] The statutory party made submissions to the effect summarised above. Those
submissions were more about the appropriateness of considering “take” issues under the
EPA rather than the Court’s lawful entitlement to consider and respond to those issues.
The statutory party stated that the Court can be satisfied that impacts on the yield of
water from MLA 70452 resulting from any take and/or interference caused by Endocoal
will be effectively dealt with through a combination of monitoring conditions in the
environmental authority, through the water licensing requirements under the Water Act
for groundwater inflows to the MDS mine pits and the current water legislative
framework for the take and interference with overland flow. That is, the statutory party
encouraged the Court to leave these matters largely to regulation under the Water Act,
rather than address them in its considerations of the environmental authority.
[56] Importantly, the statutory party did not make any submission: (1) that the Court’s
previous decisions in Xstrata and Hancock were wrongly decided and that the Court
should not follow them;14 or (2) about the consideration of “take” and “interference”
issues under the MRA.
[57] The statutory party’s amended outline does not go substantially beyond what it has
already submitted to the Court. The principal changes are:
(a) To confine the submission in paragraph 14(b) to groundwater inflows, thus
recognising that only impacts in relation to those flows will be subject to an
assessment processes under the Water Act.
(b) To make the submission in paragraph 14(c) in relation to overland flow by reference
to s 20(1)(g) of the Water Act, thus recognising that impacts in relation to those
flows will not be subject to an assessment process under the Water Act.15
[58] The statutory party’s amended outline still does not make any submissions about the
matters referred to in paragraph [56] above.
13 Statutory party’s outline, para 3.
14 The fact that the statutory party referred in paragraph 14(a) of its amended outline to the conditions of the
environmental authority as one matter that effectively addresses “take” reinforces that it was not submitted that
“take” issues are legally irrelevant.
15 As submitted below, the submissions in paras 12 and 13 of the statutory party’s amended outline now need to be
read subject to the acceptance in para 14(c) that there will be no assessment in respect of interference with
overland flow.
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22
[59] Endocoal’s further submissions go well beyond responding to the minor amendments
contained in the statutory party’s amended outline. They argue that the Court does not
have jurisdiction to consider impacts associated with the taking or interference with any
water on third party users (such as Glencore in this case) when making its
recommendations regarding the grant of mining leases or environmental authorities.16
Endocoal also specifically submits that the Court does not have the power to impose a
make good condition on a mining lease or an environmental authority.17
[60] That is, Endocoal now argues that the Xstrata and Hancock cases were wrongly decided
by the Court and should not be followed. This is the first occasion that Endocoal has
raised such an argument.
[61] Endocoal makes the extraordinary suggestion that this is consistent with its position
before the filing of its further submissions by referring to a passing comment it made in
its original written submissions in paragraph 2.10(e)9. That paragraph reads "Although
...arguably impacts on water are more appropriately dealt with under the Water Act
2000 (Qld), as submitted by DEHP" (emphasis added), before going on to state in the
same paragraph that if the Court is minded to impose a make good condition, Endocoal
has indicated a willingness to make good any impacts caused by such mining on the
quality and quantity of water in Naroo Dam.
[62] That statement is a far cry from the argument that Endocoal now makes in its further
submissions that the Xstrata and Hancock cases were wrongly decided and the Court has
no ability to consider water impacts or impose a make good condition. It is a position
also inconsistent with:
(a) Endocoal's position as advised by Endocoal to Glencore on 18 June, approximately
one month before the hearing in this case;18
(b) The evidence of Mr Darren Walker, who repeatedly asserted that Endocoal would
accept an obligation to make good the impacts of the MDS project on Naroo Dam,
and indeed was at pains to point out that it was volunteering such a condition as a
16 Endocoal’s further submissions, para 6.1(c).
17 Endocoal’s further submissions, para 3.5.
18 Exhibit DNW-3 of Exhibit 2 (being the Affidavit of Darren Walker dated 4 July 2014). The fourth paragraph of
the correspondence reads: “… We note that the ultimate position of the Land Court in those cases was that it did
not agree with the arguments run by Glencore/Xstrata and Hancock, at least to the extent that such arguments
meant that the Land Court could not consider the impact of mining activities on water supplies. The Court
determined in both cases that the impact of mining activities on water (groundwater in those cases) was a matter
that could be considered by the Land Court, and in respect of which the Land Court could make recommendations.
In both cases, the Land Court made a recommendation about the proponent making good impacted water
supplies.” The letter went on to state: “.. on the assumption that the Land Court in this case follows its previous
decisions, attached are draft make good conditions that our client is prepared to have imposed as conditions of
either the mining lease or environmental authority”.
-- 22 of 60 --
23
proposed "solution" to the impacts the MDS project would have on Glencore's water
supply at Naroo Dam;19
(c) The evidence of Mr Roads that to the extent the MDS project has an adverse impact
on water quality in Naroo Dam, Endocoal should be responsible for making good
that impact by meeting any increased treatment costs;20 and
(d) Endocoal's previous submissions in this matter,21 which specifically included
acknowledging and accepting the decisions of this Court in Xstrata and Hancock.
[63] Endocoal has sought to use its right of reply to the minor amendments contained in the
Statutory Party's Amended Outline as an opportunity to fundamentally change its
position. This is in circumstances where the Statutory Party's Amended Outline raises
nothing new about this issue. The legislation and the Xstrata and Hancock cases that
Endocoal now raises in its reply to change its position were all well known in advance of
the hearing and the filing of submissions in this matter.
[64] If Endocoal were permitted to fundamentally change its position, the impacts for these
proceedings and the related compensation proceeding will be substantial. Glencore’s case
is that the MDS project will have at least some adverse impacts on the water in Naroo
Dam, due to interference it will cause with overland flow and groundwater. These
impacts relate to the quantity and quality of water in Naroo Dam. Endocoal in its original
submissions sought to argue these were not a reason for refusal of the MDS mining lease
and environmental authority, as Endocoal would make good such impacts.22 Endocoal
has also attempted to respond to criticisms of its assessment of impacts on Naroo Dam
and the resultant uncertainty of the extent of those impacts, on the basis the Court should
take sufficient comfort that the impacts, whatever they might be, would be made good by
Endocoal.23
[65] Endocoal's position has now changed such that it says it cannot be required to make good
such impacts at all in consequence of these proceedings, and further that the Court cannot
even have regard to them. In respect of overland flow, the effect of its position is that the
impacts can never be assessed and, therefore, can never be the subject of appropriate
conditions.
19 See, for example, Exhibit 2 paragraphs 2, 6, 9, 11, 12, 14 and 16. See Transcript at T 1-21/5-20, T 1-22/5, T 1-
22/25; T 1-24/20, T 1-69/30, T 2-5/10, T 2-9/25, T 2-9/40-45 and T 2-10/45 – T 2/11-1.
20 See, for example, Exhibit 7, (Joint report of Mr Roads and Mr Scott), section 2.1 where Mr Roads agrees Endocoal
should be responsible for any increase in treatments costs required due to the adverse water quality impacts in
Naroo Dam that will be caused by the MDS project. See also Exhibit 8 (Joint report of Mr Roads and Mr
Marszalek), section 2.8.
21 Applicant’s written submissions filed on 25 July, particularly paragraph 7(3) and footnote 104; also paragraphs
7(a), 7(k), 2.8 and 2.10.
22 See, for example, applicant's written submissions filed 25 July, paragraphs 6.2(h), 6.6(a)(iv), and 6.6(d)(ii).
23 Applicant's written submissions filed 25 July, paragraph 7(a).
-- 23 of 60 --
24
[66] Apart from the impact that Endocoal’s new position has on the credibility of its previous
claims that it is willing and able to make good all impacts and has been reasonable in its
dealings with Glencore, the fundamental change of position by Endocoal seeks to directly
impact the way in which the parties have conducted their cases before the Court and the
submissions that have been made to the Court to date in relation to the merits of the
dispute. In particular, it will lead to a reopening of Endocoal's previous submissions to
the effect that impacts do not constitute a basis for refusal because they will be made
good. There must be finality to litigation.24
The Merits of Endocoal’s Further Submissions
[67] I now turn to consider the merits of Endocoal’s further submissions.
The Hancock decision
[68] In Hancock the Court concluded that s 235(3) of the MRA must be strictly applied.25
[69] I held that s 235(3) applied to circumstances where mining involves the “taking and
using of water, including the diversion of a watercourse, and perhaps, arguably, the
diversion of underground water, but not to the interference with the flow of underground
water under s206(1)(b) of the Water Act”.26
[70] I further commented that it would not be sensible for the Court to be permitted to
consider the question of any consequences which flow from interference with
groundwater, but not consider any aspect or consequence which arises from the taking or
diversion of groundwater.27
[71] I determined that both the MRA and Water Act can regulate the same subject matter,
concluding that the MRA and Water Act each have different purposes, each of which is
capable of being fulfilled.28 I also noted that this did not necessarily represent a
duplication in procedure, as the applicant for a mining lease is capable of applying for a
water licence and therefore it was within the control of the mining lease applicant to also
24 Savimaki & Ors v Sunshine Coast Regional Council [2013] QLC 33 at [28], citing the decision of the Full Court of
the Supreme Court of Western Australia's decision of Boothey v Boothey (1997) BC9700784 at page 4 where Ipp J
stated:
“In my opinion, the making of further submissions after completion of oral argument is a practice which,
ordinarily, should not occur. As a general rule, after oral argument has concluded and judgment has been
reserved, counsel should not be free to file written submissions advancing fresh or supplementary arguments. Such
a course delays the delivery of judgment, results in additional costs, is often unfair to other parties, and is
generally alien to our appeal system which is based on written outlines of argument before and oral argument
during the hearing. It is well known that at times, such as when the oral addresses have not bee [sic] completed
before the allotted time, or when a point has unavoidably taken counsel by surprise, or when a new issue arises
unexpectedly, leave will be given to counsel to make further submissions in writing, but these are exceptional
circumstances.”
25 Hancock at [117].
26 Hancock at [117].
27 Hancock at [121].
28 Hancock at [126].
-- 24 of 60 --
25
apply for any necessary water licence at the same time and have all matters heard
together.29
[72] The basis of the decision was that nothing in the relevant legislation prevented the Court
from considering issues relating to taking and interfering with water under the MRA and
the EPA and, arguably, interfering with water would not be dealt with under the Water
Act in any event.
[73] Endocoal submits that the Court in Hancock decided that “a miner as part of its
authorised activities under its mining lease, could interfere with the flow of underground
water as an activity associated with or arising from the mining without an authority
under” the Water Act.30 That submission misstates the effect of the decision.
[74] In paragraphs [105]-[111] of its reasons, I considered s 20(4) of the Water Act and
concluded that “it only applies to the diversion of water in a watercourse and not to any
aspect of underground water”. I was left in “no doubt” that should the mining activities
involve the take or use of underground water, an authority under the Water Act is
required. At para [120] I considered that it was “at least arguable” that a miner could
interfere with water without an authority under the Water Act. However, I did not
express any concluded view about that issue. Ultimately, without expressing such a view,
I concluded that I could consider the impact that the authorised mining activity had on
groundwater generally: paras [135]-[136]. It is therefore wrong for Endocoal to treat the
decision in Hancock as being based on the firm conclusion that interference with
groundwater by a miner does not require an authority under the Water Act. It was based
on the more general proposition that the activities authorised under a mining lease and
environmental authority would have impacts on groundwater and could therefore be
considered.
[75] The decisions in Xstrata and Hancock are recent decisions of the Court which address the
very issues about which Endocoal made further submissions. They are based upon the
same legislation as the Court is currently considering and are relevantly
indistinguishable. Given this, the Court should not depart from them unless persuaded
that they are clearly wrong. Nothing in Endocoal’s further submissions does that.
Water Act as a “Code”
[76] Endocoal's further submissions argue that the Water Act is a "code" for the interference
with and taking of water, and therefore the Court cannot have any regard to any water
impacts in making its recommendations regarding the mining lease and environmental
authority applications.
29 Hancock at [127] to [130].
30 Endocoal’s further submissions, para 2.1.
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26
[77] This same issue was effectively considered and addressed in Hancock. I recognised that
there was a tension between the licensing requirements of the Water Act on the one hand
and the positive pronouncement in s 234(1) of the MRA on the other as to what the
holder of a mining lease was entitled to do, with actions such as excavating mining pits
potentially having the necessary consequence of interfering with groundwater. I
concluded, after considering the Privy Council decision in Associated Minerals
Consolidated Ltd v Wyong Shire Council31 and the High Court decisions in South
Australia v Tanner32 and CMR of Police v Eaton33 that each of the MRA and the Water
Act have different purposes, each of which were capable of being fulfilled, and therefore
the Court could have regard to water impacts caused by a proposed mining project in
making its recommendation on the mining lease application and the environmental
authority.34
[78] Nothing in Endocoal’s further submissions casts doubt on the conclusions in Hancock. In
particular, the fact that a licence or other approval may be required under the Water Act
in respect of particular activity does not constitute the Water Act as a code in respect of
that activity. It is commonly the case that a particular activity is regulated by one or more
Acts with the consequence that more than one authorisation to conduct the activity is
required. The fact that authorisation under one Act is required does not mean that
authorisations under the other Acts are not required. Each authorisation is necessary but
not sufficient.
[79] Section 235(3) of the MRA and s 808(1) of the Water Act say no more than this. The
effect of s 235(3) is that a mining lease is not of itself sufficient to authorise the diversion
or appropriation of water if an authority under another Act is also required. The effect of
s 808 of the Water Act is that an authority under that Act is required to take or interfere
with water. Whether or not interference with water is within the ambit of s 235(3), s 808
is simply a particular manifestation of what s 235(3) expressly contemplated, namely that
some additional authority may be required in respect of some activities that affect water.
Section 808 does not say that if authority is granted under the Water Act, then a
requirement for an authority under any other Act is unnecessary.
[80] In the present case, the activity that will take or interfere with water is the construction of
the mine. That activity cannot occur without a mining lease under the MRA and an
environmental authority under the EPA. In the circumstances of this case, at least in
31 (1974) 2 NSWLR 681.
32 (1988-89) 161 CLR 166.
33 (2013) 294 ALR 608.
34 Hancock, paras [124] to [126].
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27
relation to the pit construction, it may also require any authority under the Water Act.
The effect of s 235(3) of the MRA is that a mining lease is a necessary, but may not be a
sufficient, authority to conduct that activity just as the effect of s 808 may be that a
licence under the Water Act is a necessary, but not a sufficient, authority to conduct it.
All relevant authorisations are required. That does not mean that any of them is a code in
the sense used by Endocoal.
[81] For Endocoal to make good its submission on this point it needs to point to some express
or implied provision to the effect that issues relating to taking or interfering with water
are irrelevant considerations under the MRA and the EP Act. It does not point to any
express provision. Nor does it advance any rational argument to the effect that such a
result is necessarily implicit in the provisions of the Water Act.
[82] The considerations to which the Court must have regard under the MRA and the EPA are
extremely broad. They do not contain any limitation of the kind suggested by Endocoal
and no legitimate process of statutory construction could result in them being read down.
Further, as I pointed out in Hancock, the activities conducted under the authority of a
mining lease will have consequences not regulated by an authority under the Water Act.
In the present case, they will include water quality issues as well as long term issues
associated with the mining of the pits. This reinforces why no relevant limitation can be
implied.
Historical analysis of the language used in s 235(3) of the MRA
[83] Endocoal's further submissions rely heavily on the history of s 235(3) of the MRA (and
the legislation that preceded it) and the evolution of the State's water legislation. It asks
that in interpreting s 235(3) of the MRA the Court should focus on the history of the
section and other legislation to give effect to a purpose that is unstated in the words of the
section itself.
[84] However, all Endocoal's analysis reveals is that once the holder of a mining lease was
entitled, under authority of that lease, to divert or appropriate water for its own use
without any further approval under the water legislation – i.e. a mining lease holder could
effectively "take" water, such as it might require for its mining operations. The
legislature then decided to change that position so that in order to divert or appropriate
water (i.e. "take" water) through mining activities, a mining lease was a necessary but not
sufficient requirement and a separate approval under the water legislation was required.
This is apparent from the extraneous material attached to Endocoal's further submissions,
such as:
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(a) The 8 March 1973 Hansard extract which states amending legislation was "… to
clarify beyond doubt that applications for and granting of water supplies for mining
purposes are to be dealt with by the Irrigation and Water Supply Commission …"
(emphasis added);
and
(b) The 23 March 1973 second reading speech extract which states "… following
proclamation of the Mining Act 1968-71, the Mines Department ceased to deal with
application for water supplies for mining purposes. The Department has suggested
the desirability of ensuring this fact is made clear … It was agreed … this objective
could be achieved by an amendment of the Water Act. A saving clause protecting
any rights to divert or appropriate water pursuant to any Act related to mining
granted prior to the commencement of the proposed amendment, is included."
(emphasis added).
[85] This point is not contentious. It was recognised in Hancock that a separate licence is
required under the Water Act to take water.
[86] Endocoal asks the Court to assume the legislature intended to "update" the language of
s 235(3) to change the words "divert" and "appropriate" to read "interfere" and "take".
However, the legislature has not made this change, and as I found in Hancock
"interference" with water is arguably something different to diverting, taking or
appropriating water.
[87] This Court in its decisions in the Xstrata and Hancock cases has given the words in
s 235(3) of the MRA their ordinary grammatical meaning. There is no reason to now
depart from that approach in this case and give them a different meaning.
Overland Flow
[88] Unlike the Xstrata and Hancock cases, in this matter the Court must give consideration to
a circumstance where activities authorised under any mining lease will interfere with
overland flow.35 It is common ground that Naroo Dam is fed by overland flow water.
Impacts, or potential impacts, on both the quality and quantity of overland flow that feeds
into Naroo Dam are in issue.
[89] Section 20(1)(g) of the Water Act permits a person to interfere with overland flow water.
Section 808(2) provides it is not an offence to interfere with overland flow water without
an approval under the Water Act.
35 "overland flow" includes water flowing over land after rising to the surface naturally from underground –
Schedule 4 Water Act 2000.
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[90] All that these provisions say is that an approval under the Water Act is not required to
interfere with overland flow. However, Endocoal’s further submissions seek to attribute a
far broader meaning to them. Endocoal submits that “no separate authorisation is now
required under the Water Act, or indeed any other Act, in relation to an interference with
overland flow” (emphasis added).36 In footnote 19, Endocoal suggests that this is also the
position adopted by the statutory party in its amended outline. However, the statutory
party’s amended outline does not contain any submission to the effect that authorisation
is not required under any other Act in relation to interference with overland flow.
[91] By making its broad submission, Endocoal asks the Court to give ss.20(1)(g) and 808(2)
of the Water Act a meaning that they simply do not have. That is not a permissible
process of statutory construction. The plain and ordinary meaning of ss 20(1)(g) and
808(2) of the Water Act is that an approval under that Act is not required to interfere with
overland flow. It is not that an approval under another Act for regulated activities that
interfere with overland flow is not required. To take the present case, that would mean
that a mining lease is not required to the extent that the proposed works interfere with
overland flow. Indeed, Endocoal’s submissions accept that ss 20(1)(g) and 808(2) were
not intended to have the effect that approvals under other applicable legislation are not
required.37 And the explanatory notes referred to in paragraph 5.3 of Endocoal’s further
submissions do not support its contention because they refer only to the absence of a
need for another authorisation under the Water Act. They do not at all indicate that the
intention was that authorisation was not required under activities regulated by other Acts.
[92] The effect of Endcoal's further submissions is that the impacts of interference with
overland flow caused by mining activities will never be assessed or conditioned. This is
because Endocoal states the Court has no jurisdiction to consider the impacts to overland
flow water under the MRA or EPA when deciding whether to recommend a mining lease
and environmental authority for grant, and the Water Act permits the impacts “as of
right”.
[93] This is an illogical result and it cannot be the legislature's intention that the impacts of
interference with overland flow would never be assessed or regulated. The dam in
question here is currently the sole source of drinking water for the Rolleston Mine's
workforce. But what if the dam in question provided water supply for the local town?
Based on Endocoal's submission, the mine's impact on the town's water supply, caused
by interference with overland flow, would be irrelevant and could not be considered in
approving the mining lease application and environmental authority, nor would it
36 Endocoal’s Further Submissions, para 5.2.
37 Endocoal’s Further Submissions, paras 5.1-5.2.
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otherwise be considered under the Water Act. It would just happen, without any checks
or balances or an ability to consider the impacts. That cannot have been intended.
[94] These matters demonstrate the incorrectness of Endocoal’s submission that no separate
authorisation is required under “any other Act” in relation to an interference with
overland flow. It also demonstrates the incorrectness of Endocoal’s submission that there
is a clear expression of intention from the State that interference with overland flow
"does not require further regulation". The sections do not say that at all. In particular,
they do not say that a Court or government authority should not consider the impacts on
overland flow of proposed developments, including mines, when deciding whether to
issue other approvals.
[95] In my view the correct position is as follows. On the basis that interference with overland
flow does not require an approval under the Water Act, s 235(5) has no possible
application because it only applies where “any Act provides that water may be diverted
or appropriated only under an authority granted under that Act”. On this basis, the
Water Act does not so provide and, pursuant to s 235(1), it is the mining lease that
authorises the activities that result in the interference. Plainly, an authorisation in the
form of a mining lease is required in respect of those activities.
[96] As authorisation is required under the MRA, in the form of a mining lease, to conduct the
activities that will interfere with the overland flow, the considerations to which the Court
must have regard are those identified in s 269(4) of the MRA. Those considerations are
broadly stated. They include adverse environmental impacts caused by the proposed
operations (s 269(4)(j)), prejudice to the public right and interest (s 269(4)(k)) and
whether any good reason has been shown for a refusal to grant the mining lease
(s 259(4)(l)). There is no legitimate basis for limiting the content of these considerations
simply because a separate approval for interfering with overland flow is not required
under the Water Act.
[97] Indeed the absence of an approvals process under the Water Act points strongly to the
need to have an assessment at this stage. As there is no approval required under the
Water Act to interfere with overland flow water, no assessment process of the impacts of
overland flow will be undertaken at a later stage. This seems to be accepted by Endocoal.
To the extent that paragraphs 12 and 13 of the statutory party’s amended outline state that
impacts on the take of overland flow are matters that will be considered in the assessment
process under the Water Act, in my view they are wrong and do not take account the
changes made to paragraphs 14(b) and 14(c) of its amended outline. Those changes are to
the effect that there will only be such a process in respect of groundwater and will not be
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such a process in respect of overland flow. Therefore, the only opportunity for such an
assessment to be undertaken, and for effect to be given to that assessment, is in
connection with the MRA proceeding.
[98] If anything, because of the interference with overland flow, and because no further
licence or approval is required under the Water Act for Endocoal to cause such
interference, there are even stronger reasons in this case than there were in Hancock for
me to consider the potential impacts of such interference in making my recommendations
about the mining lease and environmental authority.
Groundwater
[99] For completeness, for the reasons already set out, there is no reason why I should not
follow my decision in Hancock and have regard to groundwater impacts of Endocoal's
proposed mine on Naroo Dam in making recommendation regarding the mining lease
and environmental authority applications.
Conclusion on the Water Act issue
[100] There is no reason to distinguish this case from the Court's decisions in Xstrata and
Hancock, and neither Endocoal nor the statutory party has sought to do so. If anything,
the additional consideration of interference with overland flow in this case makes it an
even more compelling case than Xstrata and Hancock itself for the Court to have regard
to these water impacts in making recommendations on the mining lease and EA.
[101] I consider it appropriate to follow the decisions in Xstrata and Hancock in this case and
have regard to the adverse impacts that the MDS project will have on Naroo Dam, and
the resultant impacts on the Rolleston Mine, in making my recommendation about the
MDS mining lease and environmental authority, including in the context of making any
decision on conditions of those approvals.
Naroo Dam
[102] As can be seen from the summaries of the positions of the parties already referred to, this
case primarily relates to Naroo Dam, including issues as to the quality and quantity of
inflows of water into Naroo Dam, the dams reliability in times of drought, and the extent
to which Glencore utilises the water stored in Naroo Dam.
[103] Naroo Dam was constructed by previous owners of the land on which it is located for
agricultural purposes approximately 40 years ago, and holds approximately 745 mega
litres when full.38 The dam is located on land owned by Glencore. As the diagram set out
early in these reasons shows, Naroo Dam is overlaid by three mining tenements, being
Endocoal’s MDS MLA 70452 in the western part, Glencore’s MLA 70415 (part of the
38 See Exhibit 21 paragraphs 12 and 13.
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RCM expansion) in the centre and Glencore’s RCM ML 70307 to the east. The
constructed dam wall for Naroo Dam lies within ML 70307, and the water ponds behind
the dam wall through the relevant part of MLA 70415 and then on to the relevant part of
MLA 70452.
[104] Naroo Dam has a relatively large catchment area of approximately 10 square kilometres,
of which approximately 6.6 square kilometres lies within MLA 70452.39
[105] Having heard and reviewed all of the evidence regarding Naroo Dam, a couple of points
are abundantly clear to me. It is clear that Endocoal in making application for
MLA 70452 did so with the knowledge that it was applying over land which included
features of restricted land as defined in the MLA. There is of course nothing unusual
about that. Large open cut coal mines are almost invariably located on areas of previous
primary production activities, which invariably have many structures and constructed
areas such as dams which are technically restricted land. However, negotiations between
the miner and the landowner, if indeed the miner is not already the landowner, result
more often than not in permission being granted to use the restricted land as part of the
mining operation. I have absolutely no doubt based on the evidence before me that
Endocoal, both before and at the time of making its application for MLA 70452, thought
that Naroo Dam was nothing more than a former stock watering dam and that the owner
of the land, Glencore, would have no difficulty with such land being taken up by the
MDS.
[106] I am also in no doubt that Glencore has, since the earliest times of planning for the
RCM,40 viewed Naroo Dam as a reliable supply of raw water (meaning non mine affected
water) available for use in its RCM operations. I am also satisfied that, in times of
drought, Naroo Dam is still likely to hold water (depending of course upon the duration
of the drought), and that since the establishment of the RCM in 2002 and the resultant
use by Glencore of Naroo Dam, that Naroo Dam has never run dry, save for one incident
when the dam wall failed after some heavy downpours.
[107] For completeness, I note the evidence of Mr Roads as contained in the Marszalek/Roads
joint report, Exhibit 8, that 208 ML of pit water was pumped into Naroo Dam between
November 2012 and June 2013. I further note that in February 2014 there was predicted
to be about 210 ML of water in Naroo Dam. This gives the clear inference that, without
the pumping of pit water, Naroo Dam would have been dry, or near dry, in February
2014.
39 See Exhibit 3 p 5.
40 I note that the original planning was undertaken by MIM and subsequently Xstrata, but that Glencore has taken
over in effect those companies and retains all relevant records of the operations at RCM of MIM and Xstrata.
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[108] I also accept that the RCM since about 2010 has used Naroo Dam as its source of raw
water for obtaining a potable water supply for its employees and contractors at the RCM
site.
[109] It must also be borne in mind that Endocoal and Glencore, by the very nature of their
operations, are commercial competitors, both either already, or proposing, the supply of
thermal coal into the market. There is of course nothing at all inherently wrong in this.
However, in my view, it has tainted the actions and the evidence of both parties with
respect to issues relating to Naroo Dam.
[110] Endocoal totally underestimated the importance of Naroo Dam to Glencore at the time of
lodging MLA 70452. This caused the relationship between Endocoal and Glencore to
commence on the wrong footing.
[111] For its part, Glencore saw the MDS as a threat to its RCM operations by substantially
limiting, or perhaps effectively removing entirely, the capacity of Naroo Dam to retain
water, thus forcing Glencore to make alternate arrangements for its potable water supply.
[112] I find that not only has Endocoal originally failed to understand the importance of Naroo
Dam to Glencore, but that it continues to lack appreciation of the role that Naroo Dam
plays in the RCM operations.
[113] Conversely, I also find that Glencore, feeling under threat as it were from Endocoal’s
MDS, has over reacted and over stretched its evidence as to its reliance on Naroo Dam.
[114] Although it may seem strange, I do not find either Mr Walker or Mr Ford to have set out
to deliberately mislead the Court by giving false evidence. In my view, each of them has
had their evidence clouded, to varying degrees, by the commercial stance by their
respective employers. That has resulted in Mr Walker continuing to downplay the
importance of Naroo Dam, and Mr Ford over stretching the role that Naroo Dam plays.
For instance, I do not believe that the RCM operations, as huge as they are, would come
to an abrupt halt should, for whatever reason, Glencore be unable to source water in any
form from Naroo Dam. As Mr Ford has conceded and indeed freely set out in his
material, other options are available for water for the RCM, including sources of potable
water. If in the current wet season Naroo Dam was to again catastrophically fail and for
some reason Glencore was unable to repair the dam for an extended period of time, then
nevertheless I am sure that the RCM operations would continue so long as it remained
economically viable for it to do so, and that such economic viability would have more to
do with the market price of the coal produced by the mine rather than the ability to source
potable water.
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[115] Even though I do find that Glencore has over stretched its evidence as to its reliance upon
Naroo Dam, that does not alter the core fact. Glencore is a landholder whose land
incorporate Naroo Dam. Although there have been some questions raised as to
Glencore’s right to use the water from Naroo Dam, all parties agree that these
proceedings are not the appropriate avenue to consider issues relating to the rights of
Glencore, and I proceed on the assumption that Glencore enjoys full rights of access as
both a landholder and as a miner to the water held by Naroo Dam. It is also without doubt
that the RCM’s planned operation in their amended form will nonetheless impact upon
the ability of Naroo Dam to retain water. I also find that Endocoal has failed to adopt a
precautionary approach as to the worst case scenarios that its planned mining operations
may have on Naroo Dam. In my view, consistent with the approach I have taken in
previous cases such as Hancock and De Lacey, the EPA makes it imperative that I adopt
a precautionary approach to the utility of Naroo Dam as a source of water for its
landholder.
The Substantive Submissions of Endocoal and Glencore
[116] As Glencore has rightly pointed out in its summary submissions referred to earlier, the
circumstances of this matter are unique. One very large commercial miner (Glencore) is
seeking to continue its operations totally unhinded by a commercial competitor, whilst
another albeit smaller miner (Endocoal) is seeking to establish its own mining operations
without over concern for its competitor.
[117] I should make one observation at the outset, Mr Ambrose QC for Endocoal has submitted
that the objects of the MRA favour the grant of MLA 70452 because of the clear
Parliamentary intent to encourage utilisation of the State’s mineral and coal resources.
That is certainly true to some extent, but in the peculiar circumstances of this case the
situation is changed somewhat. In my view, it is certainly not the intention of Parliament
that the MRA should be used by a relatively small to mid size miner to impede and
disrupt the already existing mining operations of a very large miner whose RCM is
returning significant financial benefit to the State by way of royalties.
[118] Perhaps it could be said that the objects of the MRA would favour the harmonious
continuation of the RCM together with the development of MDS. Of course, harmonious
outcomes are not always achievable, particularly when, as is my duty and responsibility
in this matter, I am required to apply the law in order to give affect to a legal outcome to
the dispute between Endocal and Glencore rather than any other form of resolution that
may be commercially acceptable to each side.
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[119] It is appropriate to make an additional comment regarding the primary written
submissions of both Mr Ambrose QC for Endocoal and Mr Clothier QC for Glencore.
Both submissions are excellently written and persuasive. Not only do the submissions
show the expertise of experienced Queens Council, but they also display the extremely
high calibre of the lawyers who have supported both silk. Indeed, one can be forgiven for
reading Endocoal’s primary submissions and coming to the clear conclusion that MLA
70452 and the EA as amended should both be granted without further conditions.
Likewise, however, a detailed reading of Glencore’s primary submissions leaves one
with the clear view that both the MLA and EA should be rejected or, alternatively, but as
a clear second alternative, the MLA should only be granted with a make good condition
and the EA granted with substantial amendment.
[120] I will now turn to consider in more detail some of the primary submissions by Endocoal
and Glencore, starting with Endocoal.
[121] Endocoal makes the point in paragraph 4.5 of their submissions that, according to
Glencore’s own RCM expansion EIS, Naroo Dam is insufficient to supply the raw water
demands for the project site. This point is well made, and is consistent with my findings
of the evidence of Glencore over stating the impacts to it of a loss of water from Naroo
Dam caused by MDS. However, that is not completely the point. The RCM expansion
may never eventuate, but nonetheless Glencore would remain reliant upon Naroo Dam
for its current RCM operations.
[122] Further, although Naroo Dam may not be sufficient for all of RCM’s requirements for the
expansion project, there is a significant difference between Glencore having to find water
in addition to water sourced from Naroo Dam as part of its current operations as opposed
to having to find a completely alternate supply of water for all of its RCM operations,
including expansion operations. Furthermore, to repeat the point, Glencore as a
landholder should be able to profit from its ownership of Naroo Dam, and adjacent
mining activities must in my view take into account both the existence of Naroo Dam and
the landholder’s ability to use it.
[123] As regards paragraph 6.3 of Endocoal’s submissions, I note the comments regarding the
recommendations of the experts Merrick and Bradley regarding the collection of
additional data to enable an accurate water balance to be prepared for Naroo Dam.
Endocoal has indicated its willingness to implement this recommendation as part of a
make good condition, and I consider this to be a sensible outcome.
[124] Likewise, there were recommendations by the experts Roads and Marszalek for the
establishment of a stream flow gauging station and groundwater bores with loggers to
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monitor the rate of inflow to Naroo Dam, and an automated monitoring of Naroo Dam
water level and rainfall within the catchment to be established ahead of mining and as
soon as possible. I note that Endocoal will need Glencore’s permission to enter the
relevant parts of Naroo Dam to establish that infrastructure, but again consider these
recommendations to be appropriate and in my opinion it would be unreasonable for
Glencore to refuse access of Endocoal for the purpose of constructing and monitoring
such infrastructure.
[125] Endocoal deals with issues as to surface water quality in paragraphs 6.4 and following of
their submissions, and in particular the various expert recommendations relating to water
quality. As regards additional monitoring, Marszalek recommends that additional
monitoring for contaminants such as hydrocarbons, nutrients and pathogens should be
implemented, and Endocoal confirms that it will both comply with this recommendation
and is content for the draft EA to be amended accordingly.
[126] Experts, Roads and Marszalek, jointly recommend monitoring of water quality of inflow
to Naroo Dam and extractions of Naroo Dam be undertaken to establish base line
conditions prior to mining and to provide information on quality impacts during and after
mining, to which Endocoal responds that it will implement this recommendation as part
of compliance with any make good condition.
[127] As regards the correct construction of the dump, run off management strategies,
hydrocarbon spill management plan, investigation of risk of effluent from sewerage
treatment plant, and further data, Endocoal in essence submits that the various
recommendations of a number of the experts are part of conventional strategies for
mining operations and are already contemplated within the conditions of the draft EA. As
regards any increase in treatment cost, Endocoal41 acknowledges that experts Scott,
Roads and Marszalek recommend that any increase in treatment costs of water from
Naroo Dam that can be demonstrated to be attributable to mining on MLA 70452 should
be the responsibility of Endocoal, and says in response that it is willing to commit to a
make good condition that would require Endocoal to make good any increase in water
treatment costs attributable to any impact on water quality in Naroo Dam because of
mining on MLA 70452.
[128] I now turn to Endocoal’s submissions as to groundwater quality. As Glencore submits at
paragraph 6.8(a), there are limited matters in dispute between the groundwater experts
with the main issue remaining in dispute being the worst case scenario for groundwater
losses caused by mining on MLA 70452.
41 See Endocoal’s submissions at paragraph 6.6(d).
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[129] Endocoal’s evidence relating to groundwater quantity is that, based on the groundwater
modelling conducted, the predicted groundwater inflows into the MLA 70452 pit will
reach a peak of approximately 0.65 ML/day with an average rate of approximately 0.45
ML/day. Endocoal says that these rates are comparable to the rates of seepage that have
been seen in the active pits at the RCM, which are in the range of 1 ML/day –
1.5 ML/day. Taking into account the relative sizes of the mining operations in terms of
area, depth and geology, the modelled inflows rates to MLA 70452 are assessed to be in
a similar order to the observed inflow rates at the existing and immediately adjacent
RCM operations. Endocoal asserts that this increases the confidence in the parameters
used for the MLA 70452 groundwater model and allows for the rejection of both higher
and lower peak inflow rates that are calculated based on sensitivity analysis that are
assessed to be unreasonable based on observation of inflow rates to the RCM pits.
Endocoal notes that Mr Bradley concludes that nett loss of seepage to the Naroo Dam as
a result of mining on MLA 70452 will be in the order of 196 M³/day by end of mining
and approximately 216 M³/day in the longer term.
[130] Endocoal’s assessment of Glencore’s position is that the evidence of Dr Merrick is that
the seepage rates modelled by AGE are uncertain due to a lack of specific data. Endocoal
pointed out that Dr Merrick originally noted that use of the range of 1 ML/day –
1.5 ML/day of seepage in the RCM pits to confirm that the rates modelled for
MLA 70452 pits is flawed because seepage rates of up to 4 ML/day have been
predicative of proposed RCM expansion pits. Dr Merrick considered that the rates of
seepage into the MLA 70452 pits could be much higher than that proposed by
Mr Bradley.
[131] As regards the need for additional bores, both Dr Merrick and Mr Bradley are of the
opinion that the draft EA conditions E1 to E10 are insufficient to address potential
groundwater impacts to Naroo Dam, as there is no obligations to created new bores in
addition to the existing seven bores. Endocoal in its response said that it is planning to
install additional bores in accordance with this recommendation, and that this process has
already commenced. Endocoal says that the installation of the monitoring bores should
not be included as part of a general condition of the EA, but rather it is to be done as part
of Endocoal’s compliance with any specific make good condition.
[132] As regards monitoring equipment to be installed, both Dr Merrick and Mr Bradley state
that groundwater monitoring bores should be fitted with data loggers to allow a minimum
of data recording of changes in groundwater level. Endocoal’s response is that it has
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confirmed that groundwater monitoring bores will be fitted with data loggers that allow a
minimum of daily recording of changes in groundwater level.
[133] With respect to the setting of trigger levels, Dr Merrick and Mr Bradley recommend
setting trigger levels in the groundwater monitoring bores around the dam, based on a
given rate of groundwater level draw down over a defined period of time. They
recommended that the trigger levels should be set after data has been collected for a
minimum of six months. They further recommended that the monitoring bores be
installed, and monitoring commenced, prior to commencement of mining and ideally,
prior to the next wet season. Endocoal has responded that it will implement this
recommendation as part of risk management practices of the mine in relation to the make
good condition, noting that Endocoal has already engaged Australasian Groundwater and
Environmental consultants (AGE) to coordinate the geophysical works and subsequent
groundwater monitoring program. Endocoal also notes that it proposes to have the
additions to the groundwater monitoring network in place prior to the wet season
providing Glencore allows access to the relevant land.
[134] I now turn to consider Glencore’s submissions. Glencore’s submissions are very detailed
and extensive. Just as I did with Endocoal’s submissions, I intend in the paragraphs
below to highlight some aspects of those submissions but not refer to all of the
submissions in the interests of brevity. However, I reiterate that I have taken all the
submissions from all parties and all of the evidence fully into account in reaching my
conclusions as to the appropriate recommendation to make.
[135] Glencore points out at paragraph 16 of its primary submissions that the RCM contributes
approximately $40,000,000 to $45,000,000 per year to State royalties. RCM currently
produces 14 MTPA with an operational life to 2024. As Glencore points out, if the RCM
expansion project is approved, the rate of production will increased to 19 MTPA and the
operational life of the mine will extend to 2038. Consequentially, an expanded RCM
would also see a significant increase in State royalties paid by Glencore. The submissions
also point out, and I accept, that RCM has an accommodation village that houses up to
700 employees, with an additional village for contractors housing approximately 115
people. I further accept that in periods of peak operation, such as major shutdowns for
example, there may be more than 1,000 contractors and employees on site.
[136] In paragraph 17 of the submissions, Glencore points out that it currently obtains water
used as part of the RCM operations from three sources, being mine water, bore water,
(both used primarily for industrial purposes) and Naroo Dam, being the primary raw
water supply.
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[137] I also accept the submissions made, based on the evidence, as set out in paragraph 18 of
the submissions that the RCM currently requires the drawing of approximately 40 ML
per year from Naroo Dam. However, I am not satisfied based on the evidence provided in
these proceedings that it will necessarily be the case that a workforce of 1,000 people
will require 220 litres of water per day resulting in a consumption of approximately
80 ML per year, rising post expansion to 100 ML per year. I consider these figures over
stated for the reasons I have already stated as to the unreliability of the evidence of
Glencore’s witnesses regarding the demands on water supply from Naroo Dam.
However, that said, I am also satisfied that, should the expansion occur, Glencore will
withdraw the maximum amount of water that it possibly can from Naroo Dam as part of
its operations, whatever that amount should actually be. Doing the best I can on the
evidence before me, I consider it likely that the total draw down from Naroo Dam in any
one year will not exceed 80 ML per annum.
[138] I should point out that even a figure of 80 ML per annum is perhaps being overly
generous to Glencore, as when the raw current usage data and labour force figures are
considered, it is notable that there is current accommodation on site for some 850 or so
persons and that the current usage is 40 ML per year. On those figures, increasing the
workforce to 1,200 or 1,300 people, one would anticipate that the demands on Naroo
Dam would increase, all things being equal, to some 60 ML per year. However, I also
appreciate that an expanded RCM would put further demands on the use of water,
including industrial uses, and that RCM should be free to choose to source water for
industrial purposes from Naroo Dam as part of its operations should it choose to do so.
Thus, I have arrived at the figure of 80 ML per year.
[139] As Glencore points out at paragraph 22 of its primary submissions, it is no answer to
Glencore’s objection merely to say that it had access to a back-up supply of water
capable of treatment and use as a potable supply. As Glencore asserts, the point of the
objection is that MLA 70452 puts at risk the RCM’s primary source of the water required
to ensure its functionality. As I have already indicated, this is overstating the matter
somewhat, but nevertheless Glencore should not be in a position whereby it is required to
adopt risk merely to accommodate neighbouring mining activities.
[140] Glencore strongly asserts in paragraph 23 that it does not consider a make good
arrangement by itself is a substitute for a proper assessment of the impacts of mining on
Naroo Dam, including a substitute for the proper collection of data and assessment of that
data. For this reason, Glencore asserts that the applications should be refused, and says
that to do otherwise is to give support to the proposition that an applicant need only give
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a commitment to make good in order to secure a mining lease, in circumstances where
the potential impacts of a proposal are not fully understood.
[141] Glencore quite properly submits that the assessment of the application for the EA was
dependent upon the information provided with the application (and subsequently) by
Endocoal, and that that information did not include details as to the use that Glencore
makes of Naroo Dam. Accordingly, the environmental management plan (EMP) was
assessed, and the draft EA was provided without reference to Naroo Dam as a source of
water for potable usage. Significantly, the EMP has not be revised in view of the new
Initial Development Plan (IDP) and there has been no direct assessment of the
application for the EA on the basis of the new IDP.
[142] As Glencore submits in paragraph 38 of its primary submissions:
“This is not really a case in which expert opinion coincides, or is necessarily divided,
about the final impacts the mining proposal is expected to have upon the RCM. In
many respects, the evidence is notable for its inability to reach firm conclusions.
Endocoal’s response to this is that any risk is manageable and is being assumed by it
in the form of a make good obligation. That is neither correct nor to the point. Proper
risk management only follows proper risk assessment and it is in fact Glencore that
Endocoal risks affecting.”
[143] Glencore’s submissions then turn to issues of rehabilitation, erosion and sediment
control.
[144] As Glencore points out, the draft EA in condition H, Schedule 4 provides that slopes of
overburden dumps can be constructed up to 12°, which is approximately 20%. Glencore
properly points out that the first question that divided the expert opinion in this case is
whether 12° is likely to be achieved in the vertosol soils experienced at MDS. Glencore
relies heavily on the expert evidence given in this regard by Mr Short. As well as his oral
evidence, his expert evidence is contained within Exhibit 15, Exhibit 17, and a joint
expert report which is Exhibit 9. As Glencore notes, Mr Short is an agricultural scientist
with 20 years experience in the mining industry predominantly in Queensland and
predominantly working in black vertosol soil typical to that found at Meteor Downs.
Mr Short’s evidence is that vertosol soils are highly erodible, and that evidence is
supported by the studies by Sheridan et al. (2000) and Ahmad and Mermut (1996) and
Hayes’ Stanley (2013), Freebanirn and Wockner (1986) and Carroll et al. (2010).
[145] Glencore points out that Endocoal relies upon data derived from the Revised Universal
Soil Loss Equation (RUSLE) which was developed approximately 30 years ago based on
data from agricultural slope angles of less than 10% in the USA. Glencore submits that
RUSLE significantly underestimates actual erosion rates in mine site rehabilitation in
Central Queensland, relying upon Mr Short’s experience, his evidence, and his reference
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to the other authors as set out above. Glencore submits that care needs to be taken when
using the RUSLE model in another geographical region with different soil types and that,
at best, the results of RUSLE in the Central Queensland mining context is no more than
an indication.42
[146] I agree with Glencore’s submissions that RUSLE should be used with caution. I also
accept in this regard the evidence of Mr Short and, adopting a precautionary approach, I
agree with Glencore’s submission that reference to 12° in the EA should be removed in
this regard and replaced with 9°. In my view, this is not only consistent with the
precautionary approach as required by the environmental legislation; it is also a sensible
requirement for proper mining operations, given the nature of the soils present. Further,
Endocoal has provided no evidence or reason as to why it will be hindered in its
operations by a condition which limits the slopes of rehabilitated landforms to 9°.
[147] Before concluding this point, I should note that expert evidence regarding this issue was
of course also given by Mr Masters on behalf of Endocoal. In making my finding that 9°
slopes are more appropriate than 12° slopes, although that finding is against the evidence
of Mr Masters, I note that Mr Masters by his own admission does not have experience in
the Bowen Basin and is not therefore as conversant with the conditions in the Bowen
Basin as Mr Short. A precautionary approach demands that a careful approach should be
taken in this regard, and that careful approach requires favouring of Mr Short’s evidence
over that of Mr Masters.
[148] Neither am I persuaded otherwise by the evidence of Mr Tarlington. Mr Tarlington was
of course called by the State of Queensland to support its assessment and issuing of the
draft EA. His evidence43 was that a 12° slope is at the upper end of the spectrum in terms
of rehabilitated landforms in Queensland and that such a slope is both achievable and
will protect the environmental values downstream from the site. Importantly in my view,
Mr Tarlington agreed with the proposition put to him by Mr Clothier that generally the
approach of the department is that prevention is better than cure: you put in place the
strategies to avoid the relevant impacts first.44
[149] Glencore then turns to the second area of dispute between Mr Short and Mr Masters, that
being the longitudinal slope gradients of contour banks.
[150] In essence, the contest between Mr Short and Mr Masters is that Mr Masters’ view is that
the gradients in the contour banks should be greater than 1%, whilst in Mr Short’s view
the gradients should be less than 1%. During his oral evidence, Mr Masters stated that the
42 T 3-53/25.
43 T 3-58 L 4-7.
44 T 3-61 L 3-5.
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contour banks should be at least 1.2%.45 Mr Masters went on to state that anything less
than that is problematic with regard to issues like swell factor.
[151] Mr Short in contrast had this to say:46
“Its been my experience over many years now that contour banks, particularly when
constructed in spoil associated with the Rangal Coal Measures should be avoided. It
should be avoided because they will fail. They will fail not necessarily because of
sediment build up in them. They’ll fail because the material the banks themselves are
constructed out of is inherently highly erodible.”
[152] On balance, and taking into account Mr Short’s experience in Central Queensland, and
adopting a precautionary approach, I am more inclined to accept the approach taken by
Mr Short than that of Mr Masters.
[153] Glencore’s submissions next turn to the issue of groundwater. These submissions are
found at paragraphs 80 and following of Glencore’s primary submissions. As Glencore
points out, it relied upon expert groundwater evidence from a hydrogeologist,
Dr Merrick, while Endocoal also relied upon evidence from a hydrogeologist,
Mr Bradley. Their respective reports are set out in Exhibits 5, 6, 12, 18 and 24.
[154] As Glencore submits, the hydrogeologist experts agree on many matters. They agree in
relation to groundwater that MDS will cause less groundwater to flow into Naroo Dam,
with the potential for groundwater inflow to cease entirely and that there will also be a
loss of dam water through seepage. As Glencore rightfully submits, and as I have
previously indicated, those circumstances have the potential to cause Naroo Dam to run
dry.
[155] Glencore submits at paragraph 88 that if MDS is approved, it ought to be on the
conditions as agreed in the joint expert report, that is that prior to the commencement of
mining, groundwater monitoring bores must be installed; their data collected and
analysed to enable a baseline water balance to be prepared; and trigger levels set, the
breach of which would cause an investigation to be undertaken into the reason and
probably causative factors. I agree.
[156] Glencore’s submissions next turn to issues relating to water quality. They point out that
Mr Scott, who is an experienced geochemist with over 42 years practical experience
specialising in mine waste assessment and management, mine water assessment,
remediation and management, acid and metallifous drainage assessment and management
and mine closure, was the only geochemist to give evidence in the proceedings. As
regards Mr Scott’s evidence, Glencore forcefully submits as follows:47
45 T 2-65 L 29.
46 T 3-51 L 37-41.
47 Paragraph 91 of Glencore’s primary submissions.
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“Mr Scott stated that in his considerable experience, he has never seen a mine design
where it was proposed that run-off from mine disturbed areas would be directed into
a dam used as a potable water source (Exhibit 14, paragraph 4.1(b)), as Endocoal has
proposed to do in relation to Naroo Dam. Mr Scott further stated that in his opinion it
would be unusual for a regulator to approve for this to occur, and that best practice
mine site water management design is to ensure water run-off from mine disturbed
areas would not be directed to a potable water source (Exhibit 14, paragraph 4.1(b)).
Mr Scott’s opinion on this issue is uncontradicted, and no other expert witness gave
evidence of any example of such a situation ever being planned or approved.”
[157] Expert Roads to the contrary, called by Endocoal, indicated that he considered sufficient
information was available to define a range of potential impacts of the MDS project on
the water quality of Naroo Dam.48 Importantly, however, Mr Roads freely admitted
during cross-examination that he is not a geochemist and that he is not in a position, from
a geochemical perspective, to identify what is an adequate level of investigation and
assessment.49
[158] Clearly, the geochemical evidence of Mr Scott is uncontradicted. I accept it in its entirety
and all of Mr Scott’s recommendations and words of caution that flow in respect thereof.
[159] Glencore’s submissions next turn to the issue of water quantity. As Glencore’s
submissions point out, it relies upon expert evidence in this regard from Mr Marszalek,
whilst Endocoal relies on the expert opinion of Mr Roads. The relevant reports are
contained in Exhibits 3, 8, 13 and 16. Glencore’s submissions go on to make it clear that
in their view the expert evidence as to the impact on water quantity is not certain. In this
regard, I agree that there is some doubt as to the overall impact on water quantity that the
MDS project will have on RDS in general and Naroo Dam in particular. However, as
Glencore also submits, what is certain is that there will be an impact on the water
quantity in Naroo Dam caused by the MDS project. Again, I agree. As Glencore note at
paragraph 107 of their submissions, the evidence shows that there will be a notable
increase in the probability of a shortfall in Naroo Dam over a 9 year period whether the
Meteor Creek model or the Bootes Creek model are used. The Meteor Creek model
forecasts a decrease in reliability of 7%, or an additional 100-191 days in 9 years, whilst
the Bootes Creek model predicts a decreased reliability of 10%, or an additional 191-236
days in 9 years.
[160] It is clear enough to my mind, based on the expert evidence of Roads and Marszalek, that
the existence of the MDS project will impact on the water quantity in Naroo Dam. I am
in no doubt that, in light of this, there should be a special condition applied to
MLA 70452 if it is granted that Endocoal enter into a make good agreement with
48 Exhibit 7, paragraph 3.1, page 3.
49 T 2-48 L 10-14.
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Glencore as to the loss of quantity of water that will be held by Naroo Dam as a
consequence of the MDS project.
[161] Before leaving the submissions by Glencore as regards water quantity, it is worth noting
an agreed position as set out by Roads and Marszalek in their joint report50 as regards
monitoring. Roads and Marszalek had this to say:51
“We agree that the Draft EA conditions appear to have been developed from now
outdated MDS project plan, including monitoring points in dams which are no longer
proposed as part of the project. We agree that the additional monitoring proposed in
the Statement of Evidence by Anthony Marszalek is reasonable.”
[162] It is indeed an unusual aspect of this matter that the draft EA as approved by the statutory
party is not in fact the draft EA that either the statutory party or Endocoal contend for,
but rather the amended EA as set out in Exhibit 25. This of course has occurred as a
consequence of the new IDP by Endocoal.
Make good condition
[163] Having considered all of the evidence and submission in this matter, I am in no doubt
that it is appropriate to condition the grant of MLA 70452 on the condition that Endocoal
and Glencore enter into a make good agreement with respect to the impact that the MDS
project will have on the water supply in Naroo Dam, from both a quantity and quality
perspective.
[164] Endocoal through Mr Ambrose QC has raised concerns that requiring agreement to be
reached between Glencore and Endocoal as to the terms of a make good agreement could
be the equivalent of allowing Glencore a virtual veto of the MDL project, simply by
failing to reach agreement with Endocoal on the terms and conditions of the make good
agreement. It is certainly not my intention that the requirement to enter into a make good
agreement should be used as any form of veto by either party.
[165] In my view, this issue can be easily resolved. Section 363 of the MRA sets out the
substantive jurisdiction of the Land Court. I note in particular s 363(2)(e) that relates to
any matters arising between MLA tenure applicants or holders and owners of land in
relation to prospecting, exploration or mining. It is my clear view that should the parties
Endocoal and Glencore be required by a special condition of MLA 70452 to enter into a
make good agreement, and should those parties fail within a reasonable commercial
timeframe to reach agreement as to a make good agreement, then either party could make
urgent application to the Land Court under s 363 of the MRA to have the Land Court
resolve that dispute. I am also in little doubt that should it emerge that either party be
50 Exhibit 8.
51 Ibid at 2.9.
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shown to be unmeritorious in its negotiations for a make good agreement, appropriate
remedies would be available by way of the ordering of costs by the Land Court.
[166] Although Endocoal and Glencore have provided the Court with their respective
suggestions as to the terms of any make good agreement, in my view both parties should
be left to negotiate as between themselves the appropriate terms of the make good
agreement, taking into account of course the relevant findings in this decision. However,
by way of fundamental principle I agree with the submissions of Glencore that the make
good agreement must be such as to require Endocoal to make good any adverse impact it
causes on the quality or quantity of water in Naroo Dam as a consequence of the MDS
operation.
[167] I also agree with Glencore that the make good obligation should not be limited to a
certain volume of water or water used for certain purposes, such as potable purposes.
Further, the make good agreement should address the impacts of the MDS project post
the conclusion of mining on the MDS project.
An outcome based or prescriptive environmental authority
[168] Mr Tarlington, who was called by the statutory party, gave evidence as to the nature of
the form of drafting undertaken by the statutory party of EAs in recent times, being what
were referred to as outcome based EAs rather than prescriptive EAs.52
[169] I understand and accept the general reasoning adopted by Mr Tarlington as to the
approach taken by the statutory party in drafting relevant EAs, particularly in
circumstances where precise details as to mining programs change from time to time.
However, it is my view that, due to the unique aspects of this matter, a certain degree of
prescriptiveness is required in the draft EA to increase certainty as to the operation of the
EA, particularly from the perspective of Glencore.
[170] I also note that, in the main, the experts support amendments to the draft EA by the
addition of further conditions, some of which may be viewed as more prescriptive than
the outcome based attitude normally adopted by the statutory party. Clearly, in my view,
the system adopted by the statutory party should be flexible enough to apply more
detailed conditions when the peculiar circumstances of a particular case warrant it. This
is such a case.
[171] I accept the evidence of Mr Tarlington that in his view he has sufficiently analysed the
amended draft EA as set out in Exhibit 25 to enable to him to support that amended draft
EA as the draft EA for the Endocoal project. To that I would simply add that the
amended draft EA in Exhibit 25 should be further amended by the inclusion of conditions
52 See T 3-61 L 18 and T 3-62 L 2, and in particular T 3-61 L 20.
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consistent with those set out in the attachment to the respondent’s submissions which is
marked as Attachment 1 to these reasons.
[172] In my view, Attachment 1 is consistent with my findings relative to the expert evidence
submitted in these proceedings.
MRA section 269(4) considerations for MLA 70452
[173] When considering Endocoal’s application for MLA 70452 and the MRA objections
thereto, the Court must at all times be cognizant of the provisions of s 269 of the MRA.
In particular, s 269(4) sets out various considerations that the Court must take into
account in making a recommendation to the Honourable the Minister. I will consider
each of those elements of s 269(4) separately. My views with respect to each element of s
269(4) are based on the assumption that the MDC operates in accordance with the latest
IDP provided to the Court.
[174] Before turning to the individual elements of s 269(4) of the MRA, it is essential to
understand that, to save repetition, I will not repeat the analysis which I have already
undertaken with respect to the MRA objections. However, I must stress that, in
considering each of the criteria relevant to s 269(4) I have taken into account and
considered the relevant MRA objections made in this matter.
[175] Assistance in considering the requirements of s 269(4) of the MRA has been obtained
from Exhibit 1, Mr Walker’s first affidavit, as well as Exhibit 26, the Mining Registrar’s
report.
Section 269(4)(a) – Have the provisions of the Act been complied with?
[176] On 3 October 2013, the Mining Registrar, Emerald, issued a Certificate of Application.
The Mining Registrar can only issue the Certificate if satisfied that Endocoal is eligible
to apply for the mining lease and has complied with the requirements of the MRA with
respect to the Application.53
[177] In my opinion, there is sufficient evidence of compliance with the provisions of the MRA
in respect to this Application.
Section 269(4)(b) – Is the land applied for mineralised or are the other purposes for which the lease
is sought appropriate?
[178] I am in no doubt from the evidence presented on behalf of Endocoal that the land applied
for is mineralised in that it contains significant quantities of coal.
53 See s. 252 of the MRA.
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Section 269(4)(c) – If the land applied for is mineralised, will there be an acceptable level of
development and utilisation of the mineral resources within the area applied for?
[179] Having considered all of the evidence presented in this matter, I am satisfied that
Endocoal currently believes that it will be able to operate a profitable mining operation.
[180] The material before me shows an appropriate development and utilisation of the mineral
resources within the area applied for, taking into account the restrictions imposed by
restricted land.
Section 269(4)(d) – Is the land and the surface area of that land in respect of which the mining lease
is sought of an appropriate size and shape?
[181] The material before me appears to indicate a MLA of an appropriate size and shape in
light of the proposed mining operation, taking into account other mining tenures.
[182] I am satisfied that the requirements for this criterion have been met.
Section 269(4)(e) – Is the term sought appropriate?
[183] The term sought for this mining lease is 15 years. This period allows for an operational
extraction mine life of nine years whilst also allowing sufficient time for pre and post
mining requirements, including rehabilitation.
Section 269(4)(f) – Has the applicant the necessary financial and technical capabilities to carry on
mining operations under the proposed mining lease?
[184] Mr Walker explained the financial and technical capabilities of Endocoal this way:54
“37. Since the lodgement of MLA 70452, the Applicant became wholly owned by
U&D Mining, which is wholly owned by U&D Coal.
38. U&D Coal is a company listed on the Australian Stock Exchange, which has
the necessary funding to establish the Meteor Downs Project and a strong team
with both international and Australian resource development experience.”
[185] Although no detailed financial information relating to U&D Coal has been provided, I
am satisfied that the requirements of this criterion are met.
Section 269(4)(g) – Has the past performance of the applicant been satisfactory?
[186] With respect to this criterion, Mr Walker said that:55
“39. U&D Coal currently has one of the largest exploration tenement holdings in the
Bowen Basin. I refer to paragraph 3 of this affidavit.
40. The Applicant is in compliance with the terms of EPC 1517 (the pre-requisite
tenure for MLA 70452).
41. On or about 31 August 2012 the Applicant was issued with a notice from
DNRM directing the Applicant to remedy a breach of the conditions of EPC
1517 as a result of a the Applicant having reached agreement in ‘in-principle’
for a conduct and compensation agreement with an owner of land who
54 Exhibit 1 paras 37 and 38.
55 Exhibit 1 paras 39-42.
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subsequently sold the land without the knowledge of the Applicant. The issue
was promptly addressed by the Applicant, and resolved to the department’s
satisfaction.
42. The Applicant has not been issued with a show cause notice under the MR Act
(or the EP Act) in relation to EPC 1517, or any other tenement held by the
Applicant.”
[187] I note that what Mr Walker says is inconsistent with the applicant’s Land Court Form 9.56
However, I accept Mr Walker’s explanation for this given during his oral evidence.57
[188] I am satisfied that the past performance of Endocoal has been satisfactory.
Section 269(4)(h) – Will any disadvantage result to the holders of existing exploration permits or
mineral development licences or existing applicants for exploration permits or mineral development
licences?
[189] As Mr Walker pointed out:58
“43. There are no existing holders or applicants for exploration permits or mineral
development licences over the area of MLA 70452.
44. As mentioned at paragraph 10, at the time of lodgement of MLA 70452, an
application for ATP 756 overlapped the area of MLA 70452. As at the date of this
affidavit, ATP 756 remains under application. The Revised IDP at section 6.1
contains an assessment of the impact of development on MLA 70452 on the
development of petroleum resources from the land. The Revised IDP concludes that
the proposed Meteor Downs South Coal Project will not significantly impact on
possible future development of petroleum resources.”
[190] I agree with Mr Walker.
Section 269(4)(i) – Do the operations to be carried on under the authority of the mining lease
conform with sound land use management?
[191] As is clear from my decision thus far, I am not satisfied that the development of MDS in
terms as proposed by Endocoal in its application conform with sound land use
management as regards Naroo Dam.
[192] However, provided that MLA 70452 is conditioned to require a made good agreement
with Glencore, and that amendments to the EA in accordance with Attachment 1 are
made, then the impacts on Naroo Dam can be appropriately accommodated.
Section 269(4)(j) – Will there be any adverse environmental impacts, and if so, the extent thereof:
[193] There are certainly environmental concerns regarding the development of MDS, which is
why I am recommending a precautionary approach be undertaken.
[194] Providing that MLA 70452 is conditioned to require a make good agreement with
Glencore, and that amendments to the amended EA in accordance with Attachment 1 are
56 See Exhibit 1, DNW 12 and Exhibit 26.
57 T 1-16 L 14-1-16 L 16.
58 Exhibit 1 paras 43-44.
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made, then in my opinion adverse environmental impacts of MDS can be appropriately
dealt with.
Section 269(4)(k) – Will the public right and interest be prejudiced?
[195] It is clearly in the public interest to ensure that any mining on MDS does not impact
Naroo Dam in a way such as to put the full operation of RCM into any doubt (which
could see royalty revenue to the State from RCM fall). However, development of MDS
will also see a revenue royalty stream to the State, which is in the State’s interest.
[196] On balance, provided that MLA 70452 is made subject to a condition requiring a make
good agreement, and that the amended EA is further amended as recommended, the
public interest favours the grant of MLA 70452.
Section 269(4)(l) – Has any good reason been shown for a refusal to grant the mining lease?
[197] Reasons have been shown by Glencore for a refusal to grant the mining lease.
[198] However, as previously indicated, reasons have also been established by Endocoal to
support MDS through the granting of MLA 70452.
[199] For the reasons already given, and on the proposed conditions to the ML and the EA, on
balance I am satisfied that MLA 70452 should be granted.
Section 269(4)(m) – Is the proposed mining operation an appropriate land use taking into
consideration the current and prospective uses of the land?
[200] The materials show that the project is for the extraction of a valuable resource in
accordance with the environmental processes.
[201] My concerns relate to impacts on Naroo Dam and therefore to the follow-on impacts to
RCM.
[202] On balance, and with the proposed conditions, I am satisfied that the proposed mining
operation is an appropriate land use of the application land.
Conclusion
[203] The foregoing reasons make the orders that I propose clear. Both MLA 70452 and the
amended draft EA should be granted, but subject to conditions.
[204] Accordingly, I have decided to recommend to The Honourable The Minister responsible
for the MRA that MLA 70452 be granted, subject to the insertion of a special condition
into the mining lease that Endocoal enter into a make good agreement with Glencore,
within either twelve months of the grant of MLA 70452 or before commencement of
mining activities, whichever is the sooner.
[205] I have decided to recommend to The Honourable The Minister responsible for the EPA
that the amended EA set out in Exhibit 25 be granted, subject to amendments being made
consistent with Attachment 1 to these reasons.
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Orders
1. I recommend to The Honourable The Minister responsible for the MRA that
MLA 70452 be granted, subject to the insertion of a special condition into the
Mining Lease that Endocoal enter into a make good agreement with Glencore,
within either 12 months of the grant of MLA 70452 or before commencement of
mining activities, whichever is the sooner.
2. I recommend to The Honourable The Minister responsible for the EPA that the
amended EA as set out in Exhibit 25 be granted, subject to amendments being made
consistent with Attachment 1 to these reasons.
PA SMITH
MEMBER OF THE LAND COURT
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Attachment 1
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Official source: https://www.sclqld.org.au/caselaw/QLC/2014/054