land court of queensland registry: brisbaneenvlaw.com.au/wp-content/uploads/acland54.pdf4.32 i am...
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LAND COURT OF QUEENSLAND
REGISTRY: Brisbane
NUMBER: EPA495-15
MRA496-15
MRA497-15
Applicant: New Acland Coal Pty Ltd ACN 081 022 380
AND
Respondents: Frank Ashman & Ors
AND
Statutory Party: Chief Executive, Department of Environment and Heritage Protection
FURTHER STATEMENT OF EVIDENCE TO THE LAND COURT BY BRIAN GEORGE BARNETT
20 FEBRUARY 2017
1. Expert details and qualifications
Name
1.1 My name is Brian George Barnett.
Address
1.2 My business address is Jacobs Group (Australia) Pty Ltd of Floor 11, 452 Flinders Street, Melbourne,
in the State of Victoria.
Qualifications
1.3 I am employed by Jacobs (formerly SKM) as a Senior Groundwater Modeller.
1.4 I hold a bachelor of Engineering (Civil) (Honours), University of Auckland, 1979.
1.5 Annexure A to my first Statement of Evidence dated 10 May 2016 contains a copy of my curriculum
vitae.
2. Instructions
2.1 I have been requested by Clayton Utz to prepare a statement in relation to the 2016 IESC Final
Advice (which is attached to this statement at Annexure B) and the documentation associated with
that advice, as well as further documents finalised since that advice that are relevant to groundwater
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issues associated with the Expansion. My letter of instructions from Clayton Utz is contained at
Annexure A.
2.2 A glossary of the terms used in this statement is contained at Schedule 1 to this statement.
3. Background
3.1 I have given groundwater evidence on behalf of the Applicant in these proceedings in the following
forms:
(a) Statement of evidence dated 10 May 2016.1
(b) Joint expert report dated 11 May 2016.2
(c) Oral evidence during the hearing.
3.2 The focus of my evidence in these proceedings to date has been on aspects of the Applicant's
groundwater modelling relating to faulting. Faulting was also an important component of the 2014
IESC Advice and the 2015 IESC Advice as well as the most recent 2016 IESC Final Advice.
3.3 Shortly after giving evidence in these proceedings, I was engaged by the Applicant to attend a
meeting on 30 May 2016 between representatives of the Applicant and its groundwater consultants,
SLR, and representatives of the DoEE including a representative from the OWS. The OWS provides
secretariat and technical support to the IESC. The meeting included a status update of the
continuing work that was being undertaken in relation to groundwater issues associated with the
Expansion including work related to issues that had been previously raised by the IESC. I am also
aware through my engagement as a peer reviewer for the current model update project (referred to in
paragraph 3.6 below) that the Applicant and SLR have had further meetings with representatives of
the DoEE, OWS as well as the DNRM and, as referred to on page 2 of the Groundwater Model
Update - Phase 1 Completion Report referred to below, there has been extensive consultation with
these key stakeholders relating to the upcoming first review of the groundwater model.
3.4 The culmination of the Applicant's engagement with DoEE (including OWS) and DNRM resulted in
the Applicant providing the following additional documents to the DoEE on 24 October 2016:
(a) Fault Hydrogeological Investigation Program Report (referred to in the 2016 IESC Final Advice as "SLR, 2016a").
(b) GMIMP Status Report (referred to in the 2016 IESC Final Advice as "SLR, 2016b").
(c) Make Good Status Report (referred to in the 2016 IESC Final Advice as "SLR, 2016c").
1 Document ID: NAC.0083 (Exhibit 826).
2 Document ID: OCA.0070 (Exhibit 825).
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(d) Groundwater Model Update - Phase 1 Completion Report (referred to in the 2016 IESC Final Advice as "SLR, 2016d").
3.5 These documents (which are all annexed to this statement at Annexure C to Annexure F) are
referred to in the 2016 IESC Final Advice along with other documents that are not annexed to this
statement because they either relate to issues other than groundwater or are documents that are
already exhibits in these proceedings (refer to Schedule 2 of this statement as to a list of those other
documents).
3.6 I have been involved in a third party peer reviewer capacity in respect of the Applicant's proposal to
update its groundwater model. As part of this role, I peer reviewed the Fault Hydrogeological
Investigation Program Report and the Groundwater Model Update - Phase 1 Completion Report. I
also have an ongoing role in peer reviewing the Applicant's on-going groundwater modelling, which
will include preparation of a peer review report that will be included as an Appendix to the modelling
update report.3
3.7 Subsequent to (and as discussed in) those documents listed in section 3.4 of my statement, the
Applicant prepared the Fault Hydrogeological Investigation Program Drilling and Testing Report
which is annexed to this statement at Annexure G. This document describes pumping tests
undertaken at the Fault Investigation Site that are aimed at quantifying the hydrogeological effects of
the faults at this site. The 2016 IESC Final Advice does not reference this report because it was
completed after the submission of information to the IESC on 24 October 2016, however, it was
foreshadowed in the 2016 IESC Final Advice where the IESC said "The future work program,
including a large-scale pump testwill provide further detailed information on the groundwater
behaviour of faults within the area of groundwater impact".4
3.8 On 18 January 2017, the EPBC Approval for the Expansion was given by the DoEE. The EPBC
Approval and the EPBC Approval Reasons for Decision are annexed to this statement at Annexure H
and Annexure I. Further, prior to giving the EPBC Approval, the Minister for the Environment and
Energy provided draft proposed conditions of the EPBC Approval to the IESC for consideration. On
21 December 2016, the Chair of the IESC provided the DoEE with the IESC Chair Conditions Letter
in which the Chair of the IESC indicated that the "IESC considers that the draft conditions fully
address the matters that were raised in the [2016 IESC Final Advice]." The IESC Chair Conditions
Letter is annexed to this statement at Annexure J.
3.9 This statement includes my opinion about the significance of the groundwater reports listed in
paragraphs 3.4 and 3.7 of my statement, the IESC 2016 Final Advice, the EPBC Approval, the EPBC
Approval Reasons for Decision and the IESC Chair Conditions Letter (collectively the "New
3 Groundwater Model Update - Phase 1 Completion Report, page 9.
4 2016 IESC Final Advice, item 3a., page 3.
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Groundwater Documents"), in the context of the groundwater issues raised during the course of
these proceedings.
3.10 I have read, and am aware of, criticism of the Applicants response to the 2014 IESC Advice and the
2015 IESC Advice. In particular, I understand that there was a perception that the Applicant had
ignored the earlier advices and had not demonstrated an intention to address the IESC concerns.
For example, I have been shown the following from the transcripts in these proceedings:
(a) Professor Werner in response to a question from Mr Ambrose QC about the model:5
Its also the fact that I dont see people or the conceptualisation or the modelling even
going in the right direction to resolve them, which to me is potentially worse, because
theres so much talk about, in the future we will; in the future we will. I dont see the car
pointing down the right direction of the highway at the moment..
(b) Dr Currell in response to a question from Mr Ambrose QC about whether CG's Imposed
Conditions 10-12 address Dr Currell's concerns:6
The issue with that is that the deficiencies in this model were identified two years ago
by the IESC and they have not been substantially addressed and remedied, which to me
says theres still a great deal of uncertainty, and a lack of confidence that we can place in
this model right now. I dont see that another two years, given the lack of whats been
done over the previous two years is going to you know, I dont have confidence that
thats going to address all the concerns, based on track record. And I guess thats all I can
say.
3.11 Having reviewed the previous IESC Advices and the work that has been undertaken as outlined in
the New Groundwater Documents, I consider that there has been a continuing narrowing of the
issues from the 2014 IESC Advice through to the 2016 IESC Final Advice. In any event the IESC,
through the 2016 IESC Final Advice and the IESC Chair Conditions Letter, has clearly indicated that
it is now satisfied that all of its concerns have been addressed, including through field investigations
and modelling work that is either currently in progress or is planned and through the EPBC Approval
conditions.
3.12 In particular, the IESC has indicated its satisfaction that its residual concerns can effectively be
addressed through the proposed on-going programs of data collection, review and model updates
that are scheduled to occur following approval of the Expansion. In its previous advices, the IESC
had not indicated whether its concerns could be addressed through approval conditions but the 2016
5 T27-66, lines 26-30.
6 T10-85, lines 31-39.
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IESC Final Advice and the IESC Chair Conditions Letter has put this issue beyond any doubt.
3.13 In my view, there could be no better endorsement of the current state of the groundwater modelling
from the IESC than the following:7
The methods and data used by the proponent in their updated groundwater modelling, as described
in Question 1, are appropriate for this stage of the proposed project and consistent with industry
standards.
3.14 The message is further reinforced by the IESC when they state:8
Matters that remain outstanding could be addressed through collection of additional data before and
during operations.
3.15 Finally, the IESC Chair Conditions Letter indicates:
"The IESC considers that the draft conditions fully address the matters that were raised in the [2016
IESC Final Advice]."
3.16 From my review of the Additional Groundwater Documents, I concur with the findings of the IESC as
outlined in the 2016 IESC Final Advice.
4. The 2016 IESC Final Advice
4.1 In this section of my statement, I discuss the 2016 IESC Final Advice and provide my opinion
regarding the additional documentation which informed that advice.
4.2 My comments below make reference to the IESC's response to the various questions it was asked to
consider.
IESC Question 1
Question 1: Does the additional information reasonably address the technical/scientific matters
raised in the Departments request for additional information dated 20 October 2016, and the key
issues identified in the IESC advice (December 2015), or does it provide a robust process to address
the uncertainties relating to those matters?
Issue 1: Mapping and testing faults
4.3 The previous IESC advices indicated that the IESC considered there to be insufficient evidence to
7 2016 IESC Final Advice, bottom of page 5.
8 2016 IESC Final Advice, under the heading "Response", item 2, page 2.
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support the inclusion of faults in the groundwater model and to understand how these faults may act
to influence groundwater movement in the region of the mine.9 The IESC no longer requires that the
inclusion and parameterisation of faults in the model be resolved before approval. In my opinion, the
IESC has changed its position on this issue as a result of further information included in the Fault
Hydrogeological Investigation Program Report and the Groundwater Model Update Phase 1
Completion Report.
4.4 The Fault Hydrogeological Investigation Program Report includes a summary of the current
understanding of the faults present at the site and includes further groundwater modelling results that
have helped to illustrate the relative importance (or more particularly the lack of importance) of the
faulting included in the model. This work has highlighted the following matters:
(a) The large number of drillholes present at the site that have been used to define geological
structures including faults.
(b) The hydrogeological significance of the faults.
(c) The sensitivity of the modelling associated with the faulting.
4.5 Page 2 of the 2016 IESC Final Advice refers to Geological mapping and drilling data provided by the
proponent details the location, throw direction and strata offsets of four out of five faults10
within the
proposed project area.. In my opinion, this is referring to the following:
(a) Figure 1, page 3 of the Fault Hydrogeological Investigation Program Report (reproduced
below as Figure 1) that illustrates the number and location of drillholes constructed at the
site that have been used to help characterise the faults that are present. As indicated on
page 1 of the Fault Hydrogeological Investigation Program Report, data from almost 3000
individual drillholes have been used to define the geological model and faulting contained
within the geological model. Although there has been criticism during these proceedings
about the amount of data collected, the amount of hydrogeological information available at
the mine site is considerable and, in any event, much greater than at most (if not all)
greenfield mine sites which obtain regulatory approval on the basis that further data will be
collected during mining. Specifically, the Applicant has been able to, and continues to,
collect the following data sets that are usually not available for a greenfield mine site prior
to environmental approval:
(i) geological data obtained both from drillholes (as illustrated in Figure 1) and
from the Stage 1 and 2 mining pits. This data is being used to help identify and
9 Item 1j. on page 4 of the 2014 IESC Advice and item 12a. to c. on pages 4 and 5 of the 2015 IESC Advice.
10 I believe this phrase refers to the five faults or fault groups of substantial strike length in close proximity to the
mining pits.
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characterise faults present at the site and to help delineate the hydrogeological
units included in the model;
(ii) time series groundwater level data in bores located in and around the mine site
that help illustrate the groundwater responses that have occurred as a result of
mining. These data are being used to help calibrate the model; and
(iii) groundwater inflows into the mining pits. These data are being used to help
calibrate the model.
Figure 1 Drillhole locations at the New Acland Coal Mine (from Fault Hydrogeological Investigation Program
Report)
(b) Figures 3 to 7 of the Fault Hydrogeological Investigation Program Report that show the
interpreted hydrogeological strata on five cross sections and a map (Figure 2) showing the
locations of those cross sections. These figures are reproduced below as Figure 2 and
Figure 3.
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Figure 2 Geological cross section and fault locations (from Fault Hydrogeological Investigation Program Report)
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Figure 3 Geological cross sections showing fault displacements (from Fault Hydrogeological Investigation
Program Report)
4.6 Collectively these data illustrate that there is a large geological data set that has been used to help
define the locations and strike directions of faults present at the site. They also demonstrate that
there are substantial displacements or strata offsets associated with many of these faults. For
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example, Cross Section A-A indicates displacements of coal seams that are in the order of 80 m
across the fault.
4.7 The 2016 IESC Final Advice11
also refers to groundwater level observations presented in the Fault
Hydrogeological Investigation Program Report as evidence that monitoring results suggest that
one fault acts as, at a minimum, a partial barrier to groundwater flow. The IESC appears to
accept (correctly in my view) SLRs interpretation in this regard.
4.8 The 2016 IESC Final Advice then indicates that the IESC is satisfied that planned pumping tests
targeting this particular fault will provide useful information on the role of the fault that can be
implemented in future model updates (and not prior to approval) and provides:12
The results and methods of this study should be incorporated into the ongoing groundwater model
updates, as required by the Queensland Coordinator-Generals Imposed Condition 12 (DSDIP,
2014), and applied to other faults in the project area.
4.9 In my opinion, the evidence which supports the IESCs position is found in Table 3 and Figure 10 of
Section 4.2 on page 15 of the Fault Hydrogeological Investigation Program Report as reproduced
below as Figure 4. The table and figure illustrate that there is a head drop of approximately 5 m in
the Acland Sequence across the fault located at the Fault Investigation Site. In this regard, the IESC
conclusion supports my previous evidence on faulting,13
in that it is difficult to explain (and to model)
a head difference (and head gradient) of this magnitude in the absence of a geological structure such
as a fault that inhibits groundwater movement.
11 2016 IESC Final Advice, under the heading "Explanation", item 3 a) on pages 2 and 3.
12 2016 IESC Final Advice, page 3, first paragraph.
13 Statement of Evidence of Brian Barnett dated 10 May 2016 (Document ID: NAC.0083 (Exhibit 826), pages
25-27).
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Figure 4 Hydrogeological cross section and measured groundwater levels at the fault investigation site (from
Fault Hydrogeological Investigation Program Report)
4.10 The pumping test referred to in the first paragraph of page 3 of the 2016 IESC Final Advice has now
been completed and reported in the Fault Hydrogeological Investigation Program Drilling and
Testing Report. The pumping test results as included in that Report14
indicate that the fault acts as a
significant (but not complete) barrier to groundwater flow. It therefore reinforces the earlier
interpretation of the hydrogeological significance of this fault that had been relied upon by the IESC
in the 2016 IESC Final Advice.
4.11 I agree with the IESC conclusions with regard to this matter. I agree that there is additional evidence
that has been collected and submitted that confirms that at least some of the faults at the site act as
impediments to groundwater flow. This evidence includes the geological cross sections that illustrate
a number of faults that have substantial throw and the observed head drop across the fault at the
Fault Investigation Site. I am further reassured on this matter by the results of the pumping test as
outlined in the Fault Hydrogeological Investigation Program Drilling and Testing Report that
demonstrates that the tested fault acts as a partial permeability barrier and inhibits groundwater
movement.
14 Section 6.4 on page 46 of the Fault Hydrogeological Investigation Program Drilling and Testing Report.
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4.12 I am aware that both the pumping test and the groundwater monitoring described in paragraphs 4.10
and 4.11 above have been carried out at a location that does not align with any previously modelled
faults. This can be seen in Figure 5 below that shows the Fault Investigation Site at which the
information was obtained and both mapped and modelled faults. I do not consider the siting of the
Fault Investigation Site to be a matter of concern because:
(a) the Applicant has committed to re-conceptualise the model including the faulting as part of
the current modelling update. SLR states15
that the extent and nature of exactly how
[the faults] will be replicated, if at all, will need to be based upon the reconceptualisation
and fault testing program. The results of the assessment and the proposed methodology
for modelling will be provided in the Phase 2 report. In other words, it can be assumed
that the faults included in the next model update (currently in progress) will not be the
same as those previously included in the model;
(b) the objective of the fault investigation program is not to justify the location and character of
the faults included in superseded versions of the model. Rather, it is to provide
information on which to re-conceptualise faulting at the site with the ultimate aim of
determining an appropriate set of faults to be included in subsequent versions of the
model;
(c) the IESC has indicated that it accepts that the findings from the Fault Investigation Site
can be extrapolated to other faults in the area with significant throw. On this matter, the
IESC state:16
Groundwater behaviour and drilling information provided are for a single fault. Could be
applied to other faults with significant throw displacements (i.e. those that fully/mostly
truncate stratigraphy).
Logically this also means that, in the view of the IESC, site specific fault investigation
findings could also be applied to other locations along the tested fault provided the fault at
these locations has a significant throw; and
(d) the results of sensitivity testing shows that the faulting included in the current modelling
does not have a dramatic effect on the model results that have been used to design the
Bore Assessment Program and the Make Good Agreements (this is discussed further
below under the heading "Issue 2: Additional groundwater modelling and sensitivity
analysis").
15 At page 5 of the Groundwater Model Update - Phase 1 Completion Report, second last bullet point.
16 2016 IESC Final Advice, Attachment A, line item b).
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Figure 5 Location of the fault investigation site (from Fault Hydrogeological Investigation Program Report and
using Figure 3.0 from March 2016 IESC Response)
4.13 The matters outlined in (a) and (b) above are acknowledged in the 2016 IESC Final Advice17
where
the IESC says "The future work program, including a large-scale pump test and installation of
additional monitoring bores will provide further detailed information on the groundwater behaviour of
faults within the area of groundwater impact. The results and methods of this study should be
incorporated into the ongoing groundwater model updates, as required by the Queensland
Coordinator-General's Imposed Condition 12 ) DSDIP, 2014), and applied to other faults in the
project area." In other words, the IESC recognises that further work is required to be undertaken in
relation to faults and is satisfied that the results of this work can properly be incorporated into
subsequent versions of the model in accordance with the CG's Imposed Conditions.
Issue 2: Additional groundwater modelling and sensitivity analysis
4.14 The 2016 IESC Final Advice18
refers to modelling that is reported in the March 2016 IESC Response
and the Fault Hydrogeological Investigation Program Report.
4.15 The 2016 IESC Final Advice firstly refers to groundwater model sensitivity analysis undertaken by
AGE and reported in the March 2016 IESC Response (referred to as New Hope Group, 2016 in the
17 At the top of page 3.
18 On page 3, item 3b.
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2016 IESC Final Advice). This document describes a sensitivity analysis carried out on the faults
included in the AEIS model in which the faults were removed and models re-run to illustrate
drawdown impacts predicted without the inclusion of faults in the Walloon Coal Measures and Basalt
units. The document illustrates comparisons between predicted groundwater drawdown in the AEIS
model and in similar models in which the faults have been removed. The results of particular
relevance are presented in Figure 4.0 to Figure 7.0. These figures illustrate that the predicted extent
of groundwater drawdown in the Marburg Sandstone in particular, is not strongly influenced by the
presence of faults in the Walloon Coal Measures and Basalt units.
4.16 This modelling was the subject of criticism in the proceedings19
due to the fact that the models
without faults were not constrained by calibration. I do not accept that this criticism is valid. The
objective of the sensitivity analysis is to illustrate the impacts that faults have on the drawdown
estimates. To achieve this objective, it is important that the sensitivity model retain all model
boundary conditions and parameters other than the faults so that the resultant changes in drawdown
can be attributed exclusively to the inclusion of faults. Indeed, if the model is re-calibrated before
running the sensitivity case without faults (as the OCAA appear to suggest), then boundary
conditions and aquifer parameters will be revised to compensate for the removal of the faults. Such
changes only confound the interpretation of the sensitivity analysis as the differences in predicted
drawdown will be due to both fault removal and to the changes in boundary conditions and aquifer
parameters. The IESC specifically refers to the no fault modelling "assuming all other model
parameters and structures remaining the same" i.e. that the only change from the AEIS modelling
was the removal of faults and the model has not been recalibrated to compensate for their removal.
In this regard, the IESC appears to accept the AGE modelling outcomes in the March 2016 IESC
Response and do not share the concerns raised by the OCAA.
4.17 The 2016 IESC Final Advice also refers to separate SLR modelling results presented in Attachment
A of the Fault Hydrogeological Investigation Program Report (referred to as SLR, 2016a). The work
is similar to that undertaken by AGE as described in paragraphs 4.15 and 4.16 above. In this case,
however, I am aware that SLR has undertaken a recalibration of the models after the removal of
faults. While the results are of interest as they also suggest that the faults are not constraining
drawdown propagation in the Marburg Sandstone, they are, in my opinion, less demonstrable than
those obtained by AGE as described in paragraphs 4.15 and 4.16 above. This is because the
recalibration undertaken by SLR has led to changes in hydrogeological parameters to help
compensate for the removal of faults. Accordingly, the differences between the AEIS model with
faults and the no faults sensitivity analysis arise from both the effects of fault removal and those of
the parameter changes brought about by re-calibration.
4.18 In light of these two documents, the IESC appear satisfied that the influence of the faulting on the
19 In particular, refer to the exchange between Mr Holt QC and Mr Durick at T25-48, line 45 to T25-51, line 6.
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model predictions is not sufficient to warrant further pre-mining investigation beyond that currently
proposed (and as detailed in the Fault Hydrogeological Investigation Program Report).
4.19 In my opinion Figure 7.0 of the March 2016 IESC Response (reproduced below as Figure 6) and
Figure A12 of the Fault Hydrogeological Investigation Program Report (reproduced below as Figure
7) are important factors in forming the IESC position as documented in the 2016 IESC Final Advice.
They show comparisons between the drawdown in the Marburg Sandstone predicted by the AEIS
model with faults and without faults.
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Figure 6 Predicted groundwater drawdown in the Marburg Sandstone for the AEIS model with faults
and the no faults sensitivity analysis (being Figure 7.0, March 2016 IESC Response).
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Figure 7 Predicted groundwater drawdown in the Marburg Sandstone for the AEIS model with faults
and the no faults sensitivity analysis (being Figure A12, Fault Hydrogeological Investigation Program
Report).
4.20 Because the Marburg Sandstone is the most transmissive unit, it follows that the maximum
drawdown at most locations is predicted in this layer. Of particular relevance is the fact that the
Applicant's Bore Assessment Program and Make Good Agreements are based on the maximum
modelled drawdown in any of the modelled layers (i.e., predicted drawdown in the Marburg
Sandstone) irrespective of the layer in which the existing bores are located.20
Figure 6 and Figure 7
suggest that the predicted drawdown extent without faults is not significantly different from that
predicted by the AEIS model with faults. It therefore follows that the extent of area covered by the
Applicant's Bore Assessment Program and Make Good Agreements would not change significantly if
the no faults model were used to define this area rather than the AEIS faulted model.
4.21 While the IESC acknowledges that there are still issues that need to be resolved, it considers that the
modelling is appropriate for this stage of the project. The IESC refers to the Groundwater Model
Update - Phase 1 Completion Report throughout the 2016 IESC Final Advice. It is evidently
reassured by the forward modelling program outlined in that Report and satisfied that any continuing
issues will be dealt with by that program. Of course, the model including the conceptualisation is
also to be reviewed every 3 years over the life of the Expansion as required by the CG's Imposed
Condition 12.
20 Make Good Status Report, page 3, paragraph 2 under the heading "Baseline Assessment Program".
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4.22 I believe that the sensitivity analysis discussed in paragraphs 4.14 to 4.20 above has been important
in reassuring the IESC that the potential groundwater impacts of the mine are manageable. It is my
opinion that, before the results of this work were made available, the IESC had concerns that the
faulting included in the model was masking broader and more significant groundwater drawdown
impacts with the full extent of the masking of drawdown being undefined and unconstrained. The
sensitivity analysis results now available to the IESC have alleviated such concerns. The work has
illustrated that even when faults are removed from the model, the extent and magnitude of predicted
drawdown is not substantially greater than that previously predicted. With this reassurance, the
IESC is happy to accept that the model, even with inherent uncertainties and shortcomings, is
consistent with industry standards and that proposed and mandated upgrades to the model are
adequate to ensure that future groundwater impacts are being adequately predicted and managed.
4.23 I agree with the IESC interpretation of the significance of the model sensitivity analysis results.
4.24 I believe that the differences between the drawdown predictions in the Marburg Sandstone obtained
from the AEIS model that includes faults and from similar models that do not include faults do not
suggest that the modelled faults are acting to dramatically suppress drawdown propagation in the
Marburg Sandstone. Given the manner in which the Applicant has used the drawdown estimates to
define the properties included in the Bore Assessment Program, I believe that the model results for
the Marburg Sandstone are the most important and that model results for other aquifers are not as
important.
4.25 I do not accept that the conclusions made by the IESC on this matter are undermined or in any way
invalidated by the fact that the AEIS model with faults and the sensitivity models with no faults
include features that the IESC has previously identified as needing to be addressed and that have
been raised during these proceedings. I believe that one of the key features of the model that leads
to similar drawdown predictions in the AEIS model with faults and the no-faults sensitivity models is
the fact that the AEIS model does not include any faults in the Marburg Sandstone. I further believe
that if faults are precluded from the Marburg Sandstone aquifer in future versions of the model, then
the model drawdown predictions will continue to be relatively insensitive to the inclusion of faults in
the overlying units.
Issue 3: Groundwater modelling approach and predictions
4.26 The previous IESC advices indicated that the IESC had concerns regarding: the level of calibration
achieved,21
the choice of boundary conditions assigned to the edges of the model domain,22
the
manner in which the final void has been modelled23
and the absence of groundwater extraction from
21 Item 3, page 3, 2015 IESC Advice.
22 Items d, e and f, pages 3 and 4, 2014 IESC Advice and Item 4, page 3, 2015 IESC Advice.
23 Item w, page 6, 2014 IESC Advice and paragraph 4, page 2, 2015 IESC Advice.
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neighbouring users including those in the Oakey Creek Alluvium.24
The 2016 IESC Final Advice
addresses the following points (predominantly on page 3). I will address each of these separately in
the following paragraphs.
3a - Model Calibration
4.27 The IESC refers to the proposed approach to future model calibration described in the Groundwater
Model Update - Phase 1 Completion Report and appears to accept this as an appropriate response
to IESC concerns.25
In the IESC Chair Conditions Letter, the IESC also confirms that all of its
residual concerns have been dealt with by the conditions of the EPBC Approval.
4.28 I agree that the matters identified by the IESC as items c, d and e on page 3 and as item 6 on page
6, with respect to model calibration are being dealt with as part of the groundwater model update that
is currently being undertaken.
4.29 I also refer to paragraphs 5.7 to 5.10 of this statement as to how I consider the calibration issues
raised by OCAA in these proceedings will be addressed as part of the program proposed in the
Groundwater Model Update - Phase 1 Completion Report.
3b - Model Boundary Conditions
4.30 The 2016 IESC Final Advice states that the Groundwater model boundaries have been satisfactorily
justified.26
The 2016 IESC Final Advice also states that the proposed approach to assess the
impacts of the boundary conditions will be assessed during the planning and design stage of the
updated modelling as described in the Groundwater Model Update - Phase 1 Completion Report
(refer to Section 5.2 Numerical Modelling/Model Setup/Domain on page 6). This suggests that the
IESC is satisfied that the proposed approach will address any residual concerns.
4.31 I agree with the IESC position on this matter. I consider that the choice of head assigned to a head
dependent boundary condition at the edge of the model domain is only problematic if the modelled
drawdown responses propagate to the boundary. In most instances, the calibration process will
ensure that model boundary heads are consistent with the observed groundwater heads and with
conceptualisation of groundwater flow directions. In order to avoid undue interaction between model
boundary conditions and the groundwater responses of the Expansion, the Groundwater Model
Update - Phase 1 Completion Report27
proposes that a sensitivity analysis be undertaken on the size
24 Application of appropriate methodologies, page 2, 2014 IESC Advice and Item 6, page 3, 2015 IESC Advice.
25 Item c, page 3, 2016 IESC Final Advice.
26 Item d, page 3, 2016 IESC Final Advice.
27 Section 5.2, page 6.
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of the model domain and, if necessary, increasing the model size until the influence of the model
boundary conditions becomes insignificant. This approach is consistent with the Australian
Groundwater Modelling Guidelines which states on page 49 that In general terms the model domain
must cover the entire area of interest with, in most cases, a spatial buffer to ensure that the limits of
the model domain are sufficiently remote to reduce the impact of the assumed boundary conditions
on the model outcomes. Often it is not clear or obvious what size buffer is required. Simple analytical
models can assist with determining the expected spatial extent of groundwater responses.
Alternatively, a sensitivity analysis can be designed to test the impact of the model extent and the
selected boundary conditions on model outputs.
3c - Groundwater abstraction from neighbouring users
4.32 I am aware that OCAA suggests that the absence of the groundwater extraction from other
groundwater users was a major issue with the modelling.28
The IESC had also referred to this issue
in its previous advices.29
The 2016 IESC Final Advice30
refers to the on-going collection of
groundwater extraction data as described in the Make Good Status Report and proposed update to
the groundwater modelling as detailed in the Groundwater Model Update - Phase 1 Completion
Report. The IESC accepts that previous concerns regarding the inclusion of groundwater
abstractions will be addressed by the planned groundwater modelling as described in the
Groundwater Model Update - Phase 1 Completion Report.31
Again, the IESC (correctly in my view)
considers that this issue is being adequately dealt with in the on-going model improvement and
review process. The IESC is satisfied that a clear process has now been outlined and is under way
for including groundwater extraction from other groundwater users in the model.
4.33 I can confirm from my role as a peer reviewer for the current model update that groundwater
extraction from all identifiable groundwater users within the model domain will be included in both
calibration and predictive models.
3d - Modelling of the final voids
4.34 The IESC has identified the modelling of water quality in the final land form (including pit lakes) as a
residual issue. They note that long-term risks posed by gradual or rapid changes in water
quality(e.g. salinity pH, metals and toxicity) within final voids has not been provided. They further
suggest that This work should be informed by on-going gathering of data and information during
mining and incorporated into regular updates of the groundwater pit lake levels and water quality
28 See paragraphs 49, 936, 959, 1117-1148 of OCAA's Closing Submissions.
29 Application of appropriate methodologies, page 2, 2014 IESC Advice and item 6, page 3, 2015 IESC Advice.
30 On page 3, item 3e.
31 2016 IESC Final Advice, page 3, item 3e.
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model.32
In other words the modelling of the final voids remains an issue that should be resolved.
However, as demonstrated by the above comments, the IESC is satisfied with the Applicant
undertaking the required data gathering and modelling after approval is granted. The issue can be
addressed by the provision of a plan to acquire data and undertake the modelling.33
4.35 I agree that this issue can be effectively addressed through on-going collection of data during mining
and through more detailed modelling once these data are obtained as required by condition 18 of the
EPBC Approval. The process is in line with that described on page 12 of the Australian Groundwater
Modelling Guidelines where it is noted that The process is one of continual iteration and review
through a series of stages. and that Any number of iterations may be required before the stated
modelling objectives are met.
IESC Question 2
Question 2: Does the proponents revised groundwater modelling provide a reasonable prediction of
the expected maximum range of groundwater drawdown for the proposed mine?
4.36 In response to this question, the IESC again refers to the modelling sensitivity study that includes a
predictive model that has been constructed and run with no faults. The 2016 IESC Final Advice
indicates that the IESC considers that the envelope of predicted drawdown outcomes as defined by
the AEIS modelling and the sensitivity study modelling encompass the probable range of
groundwater drawdown that would be realised by the project.34
4.37 The IESC recognises35
that a groundwater model is a simplification of reality and that unexpected
outcomes cannot be discounted. This is true of all groundwater models and the IESC advises that
the residual risk that actual drawdown will exceed those predicted can be addressed during the
regular groundwater model updates process required by the regulator and through ongoing
monitoring and refining hydrogeological characterisation.36
In my opinion, the planned program of
data collection and model updates will lead to an increase in the confidence in model predictions, in
particular, the inclusion of additional calibration data through the use of groundwater head and flux
observations collected during mining. As model confidence increases and uncertainties decrease
the chances that groundwater responses to future mining will deviate substantially from modelled
predictions will be reduced.
32 2016 IESC Final Advice, page 4, item 4a.
33 Also refer to condition 18 of the EPBC Approval conditions which were approved by the IESC as described in
the IESC Conditions Letter.
34 2016 IESC Final Advice, page 5, item 5.
35 2016 IESC Final Advice, page 6, item 6.
36 2016 IESC Final Advice, page 6, item 6.
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4.38 In the GMIMP Status Report that was considered by the IESC, SLR acknowledged that as a result of
the model update process, the groundwater predictions may be different to those derived from the
AEIS 2014 model and this may result in the requirement to change the locations of monitoring
bores.37
Again SLR, like the IESC, is merely confirming that a groundwater model is a simplification
of reality and that unexpected outcomes cannot be discounted.
IESC Question 3
Question 3: Are there any additional management measures that may be implemented to better
address the above matters?
4.39 In response to this question, the IESC38
notes that there are still some residual issues that have not
been fully addressed. However they state on page 6 that A range of measures to mitigate, manage
and monitor the residual concerns is provided below. If the proposed project is approved, these
measures could be undertaken prior to commencement of, or in some instances during, mining. In
other words the IESC is satisfied that the process required to fully address all outstanding matters
can be undertaken after approval and prior to or during mining.
4.40 These issues are dealt with in the EPBC Approval conditions referred to below. Condition [13xiii.] of
the EPBC Approval states that the GMMP must address the groundwater management measures
outlined in the 2016 IESC Final Advice. Condition 16 provides that the approval holder must
undertake groundwater model reviews in accordance with the requirements of the CG's conditions
and requires that the reviews must address all matters raised in the "December 2015 and 2016 IESC
advice" in regards to groundwater modelling.
4.41 Further as outlined in paragraph 3.8 of this statement, in the IESC Chair Conditions Letter, the IESC
indicated:
"The IESC considers that the draft conditions fully address the matters that were raised in the [2016
IESC Final Advice]."
2016 IESC Advice Attachment A
4.42 In Attachment A to the 2016 IESC Final Advice, the IESC tabulates a summary of matters requested
by DoEE in October 2016. The following items from that Attachment are related to the faulting,
groundwater modelling and the matters that I have referred to above.
37 GMIMP Status Report, page 6 (note that the report contains "page 8" on each page in error).
38 2016 IESC Final Advice, page 6.
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4.43 Item a) Local geology, including faults which impact on how groundwater impacts move away from
the mine. This line of the table is shown below:
The IESC considers the matter to have been addressed and refers to the fault mapping and fault
testing program described in paragraphs 4.3 to 4.9 of this statement. The IESC recognises that the
model with a southeast strike needs to be verified (tested further), however running the model
without faults addresses this uncertainty. The response clearly demonstrates that the IESC does
not share the concerns of Professor Werner and Dr Currell regarding the manner in which the faults
have been modelled and the importance of the faults. The IESC note that the no-faults model
outcomes provide a valuable perspective on the importance of faults in the model and the results
used for on-going make-good measures. I agree with the IESC on this matter.
4.44 Item b) Groundwater monitoring including faults which impact on how groundwater impacts move
away from the mine. This line of the table is shown below:
Here the IESC refers to the results in the Fault Hydrogeological Investigation Program Report for a
single fault. It should also be noted that the recent pumping tests undertaken near the fault (as
outlined in the Fault Hydrogeological Investigation Program - Drilling and Testing Report which had
not been completed at the time of the IESC advice) have demonstrated that this fault indeed does act
as a partial barrier to flow confirming the preliminary findings in the Fault Hydrogeological
Investigation Program Report that was considered by the IESC. The IESC accepts that the proposed
fault testing program is appropriate. Of note is the indication that the IESC considers that it is
suitable to extrapolate findings for one fault to others with significant throw displacements, and that
the fault testing results should be incorporated during model updates required by the CGs Imposed
Condition 12 and is not required prior to approval. I believe that this is an appropriate response to
this issue. The only practical means of testing and verifying fault behaviour is through a program of
mapping strata across faults, measuring head differences across faults and, if necessary undertaking
pumping tests with observations on both sides of the faults. In my opinion, the degree to which a
fault will act as a barrier to groundwater flow will depend on the displacement of geological strata
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across the fault. In this regard it is perfectly reasonable and appropriate to apply the findings at one
fault investigation site to other faults, or parts of faults, that display similar levels of displacement.
4.45 Item c) Groundwater monitoring including the timeframes for an update and more conservative
estimates of impacts. This line of the table is shown below:
The no-faults sensitivity analysis is again referenced here. The IESC notes that the final void
modelling including water quality modelling is an outstanding issue that will need to be resolved.
This is dealt with in the conditions of the EPBC Approval referred to below.
Other matters
4.46 In this statement, in relation to the documents that were provided to the IESC, I have predominantly
referred to the Fault Hydrogeological Investigation Program Report and the Groundwater Model
Update - Phase 1 Completion Report. Two other important reports, namely the Make Good Status
Report and the GMIMP Status Report were also provided to the IESC.
4.47 The Make Good Status Report indicates that the Applicant's baseline assessment program is very
well advanced. The IESC noted this in line item f) of Attachment A to the 2016 IESC Final Advice
and indicates that this program will provide contextualisation of regional water resources through the
collection of accurate information on both groundwater allocations and the actual use of groundwater.
4.48 As indicated in paragraph 4.20 of this statement, the Make Good Status Report also indicates that
the Applicant's baseline assessment program and Make Good Agreements are based on the
maximum modelled drawdown in any of the modelled layers (i.e. predicted drawdown in the Marburg
Sandstone) irrespective of the layer in which the existing bores are located. 39
This is a conservative
approach and provides additional protection to landowners. Even if landowner bores would otherwise
not be included in such a program because they are in aquifers that have predicted drawdown less
than the trigger value to activate the baseline assessment program, the Applicant has nevertheless
included such landowners in the program. In addition, in the last paragraph of section 2.1 of the
Make Good Status Report, it is noted that even where landowners are outside of the predicted trigger
39 Make Good Status Report, page 3, paragraph 2 under the heading "Baseline Assessment Program".
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value drawdown extents, where those landowners have expressed concerns, the Applicant has
included those landowners in the baseline assessment program.
4.49 The GMIMP Status Report indicates that the Applicant has already installed all monitoring bores for
the Expansion following an extensive drilling program from 2014 - 2016. Further, as indicated in
paragraph 5.13(a) of this statement, the monitoring network includes the utilisation of paired
monitoring bores to assess inter-aquifer connectivity. Section 4 of the GMIMP Status Report also
indicates, properly in my opinion, that refinement of this network may be required following future
model updates if predicted drawdowns change. In my opinion, this is an appropriate approach that is
consistent with the notion that the model may be revised through future validations and iterations.
4.50 I consider that the advanced state of both the baseline assessment program and the groundwater
monitoring network also indicates that groundwater issues are being given prominence by the
Applicant and further support the IESC's position (which is also my position) that the available data
and the status of the groundwater modelling undertaken by the Applicant are appropriate for this
stage of the proposed project and are consistent with industry standards.40
Changes to the composition of the IESC
4.51 The IESC membership has changed over the period in which it has provided advice on the proposed
Expansion. At the times of the 2014 and 2015 advices, from my knowledge and understanding of the
committee members, the only committee member with groundwater modelling skills and experience
was Professor Simmons of Flinders University. I can confirm that Professor Simmons is a widely
respected academic and teacher of groundwater science.
4.52 At the time of the 2016 IESC Final Advice, two additional groundwater scientists were added to the
committee. Dr Wendy Timms of the University of New South Wales and Dr Glen Walker, formerly of
Land and Water Division of CSIRO joined the committee. The curriculum vitae of each of Dr Timms
and Dr Walker from the IESC website are annexed to this statement at Annexure K. Dr Timms and
Dr Walker bring a great deal of practical, as opposed to academic, experience to the committee.
They are experienced groundwater practitioners and are well respected in the groundwater
community. I believe that the addition of Dr Timms and Dr Walker to the committee has resulted in a
different perspective on the modelling that has improved the relevance and quality of the advice.
Summary of my opinion on 2016 IESC Final Advice
4.53 In my opinion, the 2016 IESC Final Advice is largely based on the following evidence and logic:
(a) It has been established that faults present at the mine site act as impediments to
groundwater flow. This is based on the following:
40 2016 IESC Final Advice, item 5 on page 5.
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(i) A series of geological cross sections have been provided that illustrate
significant displacements across faults that have been mapped at the site.
(ii) Groundwater heads measured in bores on either side of one of those faults
indicate a significant head difference across the fault (as illustrated in Table 3
and Figure 10 of the Fault Hydrogeological Investigation Program Report as
reproduced in Figure 4 above). It is also important to note that subsequent to
the 2016 IESC Final Advice a pumping test carried out at one fault location (as
reported in the Fault Hydrogeological Investigation Program - Drilling and
Testing Report) illustrates that the fault acts as an impediment to groundwater
flow.
(b) The results obtained from the Fault Investigation Site can be extrapolated to other faults
that have significant displacements. It follows that the result can equally well be
extrapolated to other locations along the tested fault provided the displacement is
significant.
(c) Recent sensitivity analysis modelling that has been undertaken with the faults removed
from the model has illustrated that the extent of drawdown impacts, as used to define the
properties at which make-good measures may be required, is similar in both the AEIS
faulted model and in the no-fault sensitivity analysis.
(d) The IESC has indicated its satisfaction that the no-faults sensitivity analysis is likely to
represent the upper limit of the envelope of modelling outcomes that may arise from the
uncertainty in the fault locations and fault properties used in the modelling while properly
acknowledging that "there will always be some residual risk of drawdown extending
beyond the bounds presented in the modelling." Accordingly, the IESC accepts that at the
likely upper limit of the uncertainty envelope, the drawdown impacts can be managed
within the existing monitoring and make-good measures currently being implemented by
the Applicant. The IESC has therefore concluded that the exact location of, and properties
assigned to, the faults do not exert a significant influence on modelling and project
outcomes.
(e) The IESC acknowledge that, in line with the Queensland CG's Imposed Condition 12, the
Applicant has outlined a plan of on-going field investigations, data collection and
upgrading of the groundwater model. The IESC has confidence that any remaining
concerns around the validity of the modelling can be adequately addressed through this
process.
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4.54 I am in full agreement with the IESC on all of the above and consider that the findings in the advice
accord with current industry and regulator expectations and standards on the use of groundwater
models to assess future impacts of mining operations.
5. Will matters identified during these proceedings be considered as part of the model review
contemplated in the Groundwater Model Update - Phase 1 Completion Report?
5.1 As noted on page 2 of the Groundwater Model Update - Phase 1 Completion Report, a working
group (including myself) has undertaken a thorough analysis of groundwater modelling issues raised
in the Land Court process.
5.2 In my opinion, the Applicant's program of works as outlined in the Groundwater Model Update -
Phase 1 Completion Report addresses the issues that have been raised in these proceedings.
5.3 This program, as required by the CG Imposed Condition 12(c), requires a comprehensive update of
the model, which includes a full review of the hydrogeological conceptualisation. I note that the
Applicant has proposed that the first review of the groundwater model occur prior to mining (and after
the collection of certain further data), which is earlier than that proposed by the CG.41
5.4 The EPBC Approval conditions also require the Applicant to undertake groundwater model reviews in
accordance with the CG's Imposed Conditions and such reviews must address all matters raised in
the 2015 IESC Advice and the 2016 Final IESC Advice. These conditions are discussed in more
detail in section 6 of this statement.
5.5 The IESC has reviewed the program of works in the Groundwater Model Update - Phase 1
Completion Report and is clearly comfortable with the approach and progress to date, as indicated
by the following comment: 42
The methods and data used by the proponent in their updated groundwater modelling, as described
in Question 1, are appropriate for this stage of the proposed project and consistent with industry
standards.
Examples of how the model review contemplated in the Groundwater Model Update - Phase 1
Completion Report addresses OCAA's issues
5.6 In this section, I identify some examples of how, in my opinion, the Applicant's program of works for
the groundwater model update, as outlined in the Groundwater Model Update - Phase 1 Completion
Report, adequately addresses the issues that have been raised by OCAA's groundwater experts in
these proceedings. In particular, I have been asked to comment on the issues raised in paragraphs
41 Applicant's Reply Submissions, condition 2(a) on page 293.
42 2016 IESC Final Advice, item 5, page 5.
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69 to 84 of OCAA's IESC Submissions (on the admissibility of the 2016 IESC Final Advice) as being
issues OCAA suggests have not been resolved in the 2016 IESC Final Advice.
Model calibration issues
5.7 In paragraphs 69 to 73 of OCAA's IESC Submissions, OCAA questions whether issues raised in the
2015 IESC Advice regarding calibration are being adequately addressed in the current modelling.
The submission focuses on the fact that the IESC refers to improvements in model calibration in the
Alluvium and questions whether such improvements can also be expected in the Walloon Coal
Measures.
5.8 The Groundwater Model Update - Phase 1 Completion Report outlines generally the approach to
calibration that will occur as part of "Phase 3" of the groundwater model update.43
The document
outlines calibration objectives, calibration targets (including the weights assigned to each target) and
the proposed Monte Carlo approach to calibration. There is no specific reference in this report to
calibration methods or targets in the Alluvium or Walloon Coal Measures or any other
hydrogeological unit present in the model. I can confirm that the measures taken to improve
calibration will apply equally to all hydrogeological units. The 2016 IESC Final Advice on model
calibration refers specifically to improving calibration in the Alluvium suggesting that this is the focus
of its concern. I believe that the IESC has referred specifically to the Alluvium and to alluvial bores
as the IESC considers that the inclusion of groundwater extraction in the model is a key component
that will lead to an improved calibration. The addition of groundwater extraction to the model will
probably have the biggest effect on the Alluvium model layer which hosts a high level of groundwater
extraction.
5.9 Further, I have been asked to consider the other issues relating to the model's calibration in OCAA's
Closing Submissions.44
In my view, these issues will also be addressed as part of the proposed
approach to calibration of the model that will occur as part of "Phase 3" of the groundwater model
update.
5.10 For example, an issue raised in OCAA's Closing Submissions was that the number of realisations of
the model (18) was too small.45
This issue is expressly dealt with in the Groundwater Model Update -
Phase 1 Completion Report where it is stated that "at least 40 calibrated realisations" will be
established as part of the model review. This issue was also referred to by the IESC at item 6d. of
the 2016 IESC Final Advice. I can also confirm that more realisations than 40 will be used should
they be found to fit the agreed calibration criteria. Other issues raised by OCAA during these
43 Pages 7 to 8 under the heading "Regional Model Calibration".
44 For example, see OCAA's Closing Submissions, section 8.9 "Model is poorly calibrated" starting on page 298.
45 OCAA's Closing Submissions, paragraphs 1168 to 1171, pages 297-298.
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proceedings relating to recharge and specific storage values were also referred to by the IESC at
item 6a. of the 2016 IESC Advice. Again, the IESC does not consider that these issues have to be
resolved before approval but, in my view correctly, consider that they can be addressed through
appropriate approval conditions. Such improvement and refinements over the life of a project and
associated groundwater model is standard practice.
Other groundwater users
5.11 I also refer to paragraphs 4.32 and 4.33 of this statement regarding my view that the current
groundwater modelling update will include groundwater extraction from all identifiable groundwater
users within the model domain in both calibration and predictive models. This addresses a key
concern raised by OCAA during the proceedings. As noted in those paragraphs, the IESC again is
satisfied that this issue can be dealt with through the current and planned groundwater modelling and
through conditions of approval.
Issues raised in paragraphs 74 - 77 of OCAA's IESC Submissions
5.12 In paragraphs 74 to 77 of OCAA's IESC Submissions, OCAA suggests that there are "key issues that
appear to be overlooked in the IESC 2016 Advice". In my view, the Groundwater Model Update -
Phase 1 Completion Report and the various conditions imposed on the Expansion address the
proposed process for dealing with these issues in the next update of the groundwater model.
Accordingly, rather than those issues having been overlooked, they have either been fully addressed,
are in the process of being addressed as required by conditions of approval, or are no longer
considered of significance by the IESC in light of other information that the Applicant has supplied. I
do not believe that the IESC could issue this advice nor the IESC Chair Conditions Letter if there
were any substantive concerns that had simply been overlooked. Any suggestion that the IESC
has overlooked issues raised in its 2014 and 2015 advices is, in my opinion, not plausible.
5.13 Below I give some examples as to how issues identified by OCAA have been, or are being
addressed:
(a) In paragraphs 80(a) and (b) of OCAA's IESC Submissions, OCAA questions the evidence
base for conceptualisation and modelling of the vertical connection between key aquifers
as well as the assignment of aquifer properties to key units. Further on this issue, the
IESC notes in the 2016 IESC Final Advice that the final GMMP should include "an outline
of the proposed methodology to assess groundwater connectivity between each
hydrogeological unit using nested bore arrays..". This is reflected in the EPBC Approval
conditions, which the IESC considers is the appropriate manner to address these issues.
The Groundwater Model Update - Phase 1 Completion Report outlines the additional data
to be collated as part of the model update process. The report then outlines that, as part
of "Phase 2" of the model update process, there will be an analysis and discussion of
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various data including groundwater gradients and flow directions and aquifer hydraulic
testing.46
The evidence base for the conceptualisation and modelling of the vertical
movement of groundwater and the connections and flow between aquifers as well as the
assignment of aquifer properties to all hydrogeological units is being reviewed as part of
"Phase 2" and will be incorporated into the groundwater model during Phase 3 of the
update. Further in section 5 headed "Inter-aquifer Connectivity" of the GMIMP Status
Report, it is noted that the already installed monitoring network "includes the utilisation of
paired monitoring bores to provide monitoring of vertically stacked aquifers within and
immediately surrounding the Project site. These include the alluvium, basalt, Marburg
Sandstone aquifers, as well as the other Walloon Coal Measures units above and below
the target seams of mining. .These bores will allow assessment of vertical hydraulic
gradients between aquifers prior to commencement of Stage 3 mining, and ongoing
monitoring during the Project will allow assessment of any changes to these gradients as
a result of mining. Furthermore, if changes in vertical gradients are measured during the
Project, these measures can be used to provide an estimate of potential groundwater take
through analytical or numerical modelling".
(b) In paragraph 80(c) of OCAA's IESC Submissions, OCAA questions the quality of the
calibration data (such as pit inflows data) and the evidence base for groundwater recharge
and discharge. This data is addressed by the Groundwater Model Update - Phase 1
Completion Report which outlines the additional data collated as part of the "Phase 1"
process. This includes groundwater inflow records for the Stage 1 and 2 mining pits as
well as other information that will form the evidence base for the re-conceptualisation of
the model in "Phase 2" and the model update in "Phase 3". The groundwater pit inflow
calibration targets are being reviewed and, if required, will be updated as a part of this
work.
(c) In paragraph 80(d) of OCAA's IESC Submissions, OCAA questions the calibration method
and uncertainty analysis. As is noted in paragraph 5.8 of this statement, the Groundwater
Model Update - Phase 1 Completion Report outlines generally the approach to calibration
of the model that will occur as part of "Phase 3" of the groundwater model update. The
document outlines calibration objectives, calibration targets (including the weights
assigned to each target), the proposed Monte Carlo approach to calibration and the
information that will be provided in support of the calibration results (including a summary
of calibration sensitivity and uncertainty for parameters used in the Monte Carlo process).
The issues raised by OCAA will be addressed through this process.
46 Groundwater Model Update - Phase 1 Completion Report, page 5.
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Faulting
5.14 A key issue of focus for OCAA in OCAA's Closing Submissions was the role of faulting in the
model.47
OCAA also raised this issue in paragraphs 82 to 84 of OCAA's IESC Submissions.
5.15 I have already outlined above in section 4 of this statement my conclusions about the additional
information provided to the IESC in respect of faulting. Further to that information, I also note the
following:
(a) The Groundwater Model Update - Phase 1 Completion Report notes at page 5 that the
extent and nature of how faults will be replicated in the revised model will be based on the
re-conceptualisation as informed by the fault mapping and testing program, the results of
which will be provided as part of "Phase 2".
(b) The Applicant has proposed an amendment to the draft environmental authority conditions
to require further information and investigation of faults.48
(c) The Applicant has proposed a further condition on ML 50232 that the groundwater model
review (which is to occur prior to mining and in accordance with the Applicant's condition
referred to in paragraph 5.3 of this statement) must include updated information about
faulting based on the data collected under the condition described in paragraph 5.15(b) of
this statement.49
(d) The EPBC Approval conditions expressly require the groundwater model update to
include "validation of the existence and nature of faulting and its potential effect on the
predicted lateral extent of groundwater drawdown".50
5.16 I believe that these conditions, as well as the additional information about faulting that is described in
section 4 of this statement and in the Groundwater Model Update - Phase 1 Completion Report, will
ensure that the next iteration of the groundwater model (and subsequent updates of the model)
appropriately characterise the role of faults and properly represent these features in the numerical
model.
47 For example. see OCAA's Closing Submissions, section 8.6 "Faulting in the model is unjustified and affects
model predictions", from page 259.
48 Applicant's Reply Submissions, condition D15(d) on page 287.
49 Applicant's Reply Submissions, condition 2(b)(iii) on page 293.
50 EPBC Approval, condition 16(i) on page 5.
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6. EPBC Approval - Conditions
6.1 In my view, the EPBC Approval contains key groundwater conditions that, along with the extensive
groundwater conditions already imposed through the CG's Imposed Conditions, the Draft EA
conditions and the additional conditions proposed by the Applicant during the proceedings, provide a
high level of protection for the objectors in these proceedings. This is confirmed by the Minister for
the Environment and Energy throughout the EPBC Approval Reasons for Decision.51
The IESC also
confirms in the IESC Chair Conditions Letter that the conditions proposed by the Minister for the
Environment and Energy address all of the IESC's residual concerns.
6.2 In particular, I note the following key conditions:
(a) Condition 12 which provides that the Applicant must submit a GMMP to the Minister for
written approval and that mining activities must not commence until the GMMP has been
approved by the Minister in writing. This approval is in addition to the approval required to
be provided by the DNRM under the CG's Imposed Condition 10 (in respect of the
equivalent plan).
(b) Condition 13c. requires sufficient bores to be installed to determine the lateral extent of
groundwater drawdown and flow direction, to monitor potential impacts on groundwater
resources and the effect of faulting on groundwater drawdown. With respect to faulting,
this condition complements condition D15d) proposed by the Applicant in the Applicant's
Groundwater Conditions.52
(c) Condition 13x. which provides that the GMMP must include "mechanisms for addressing
the impacts of the action to groundwater resources, including details of measures for
impacts to water bores, and offsets for the Oakey Creek Alluvium and Tertiary Basalt
Aquifer".53
Such offsets for the Oakey Creek Alluvium and Tertiary Basalt Aquifers "may
comprise a retirement of part or all of an existing entitlement, or purchase and retirement
of a new entitlement".54
(d) Conditions 13ii. and iii. regarding baseline monitoring.
(e) Conditions 13iv. and v. which provide that the GMMP must contain monitoring bores to be
used as early warning indicators of groundwater drawdown propagation and threshold
51 Refer paragraphs 56 to 92 and 103 in particular.
52 See page 287 of the Applicant' Reply Submissions.
53 EPBC Approval, page 4.
54 EPBC Approval, page 9.
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triggers for these early warning monitoring bores.
(f) Condition 13A which provides that, if monitoring reports, based on threshold triggers for
early warning monitoring bores, indicate that a groundwater drawdown limit will be
substantially exceeded, the Minister may require the Applicant to suspend its mining
operations. This condition was specifically referred to by the Minister for the Environment
and Energy in the EPBC Approval Reasons for Decision.55
(g) Condition 14 which provides that the Minister may submit the GMMP to the IESC or other
independent expert for review before making a decision on whether to approve it under
condition 12.
(h) Condition 16 which provides that the Applicant must undertake groundwater model
reviews in accordance with the requirements of the CG's conditions and requires that the
reviews must address all matters raised in the "December 2015 and 2016 IESC advice" in
regards to groundwater modelling. It is also important to note that the Applicant's
proposed groundwater conditions require the model to be reviewed earlier than that
required by the State and Federal regulators (with the first review to occur prior to any box
cut excavation - in particular, I refer to condition "2 Collection of data and groundwater
model review" located at page 293 of the Applicant's Reply Submissions). The result of
this is that the revised groundwater model is expected to be available for the associated
water licence application process for the Expansion.
(i) Condition 22 which requires that, within three months of every 12 month anniversary of
the commencement of the action, the Applicant must publish a report on its website
addressing compliance with each of the conditions of the EPBC Approval. Documentary
evidence providing proof of the date of publication must be provided to the DoEE at the
same time as the compliance report is published. Reports must remain on the approval
holders website for the duration of the approval.
(j) Condition 23 which requires that the Applicant must report any contravention of the
conditions of this approval to the DoEE within 2 business days of the Applicant becoming
aware of the contravention.
(k) Condition 24 which requires that upon the direction of the Minister, the Applicant must
ensure that an independent audit of compliance with the conditions of approval is
conducted and a report submitted to the Minister. The audit must not commence unless
and until the Minister has approved the independent auditor and audit criteria. The audit
report must address the criteria to the satisfaction of the Minister.
55 Refer paragraph 79.
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(l) Condition 28 which requires that, unless otherwise agreed to in writing by the Minister, the
Applicant must publish all management plans referred to in these conditions of approval
on its website. Each management plan must be published on the website within 1 month
of being approved by the Minister or updated and remain available on that website for the
life of the approval.
7. Overall Conclusion
7.1 The information recently provided to the IESC for consideration (as listed in paragraph 3.4 of this
statement) has helped to reassure the IESC that the Applicant is addressing its previous concerns.
This is largely through the Applicant gathering data that helps clarify the location and hydrogeological
function of the faults and illustrating that the inclusion of faults in the Walloon Coal Measures and
Basalts is not unduly masking a much broader propagation of drawdown impacts. It is clear that the
IESC is now happy that their remaining groundwater modelling concerns are being addressed and
will be addressed through the program of model updates that is currently under way. In this regard,
the IESC appears confident that the potential groundwater impacts associated with the planned
Expansion can be adequately managed through the planned work program and through the
implementation of numerous conditions attached to the approvals.
7.2 In my view, the additional investigations, modelling (both that planned and completed) and
interpretations that have been provided to the IESC illustrate a continuation of the iterative
groundwater modelling process that commenced with my work in 2009. The conditions both at a
State and Commonwealth level ensure that this iterative process will continue for the life of the
Expansion. I believe that confidence in the model predictions will increase with every update and
iteration of the model.
7.3 I consider that the Additional Groundwater Documents provide clear evidence that groundwater
issues are being appropriately managed for the Expansion and there is a clear strategy moving
forward with the groundwater modelling. Using the words of Professor Werner that I set out in
section 3 of this statement, it is clear from the New Groundwater Documents that "the car is pointing
down the right direction of the highway" in terms of the groundwater model for the Expansion. That is
reflected in the 2016 IESC Final Advice and the IESC Chair Conditions Letter where the Chair of the
IESC provided advice that the proposed conditions of the approval fully address the matters that
were raised by the IESC in the 2016 IESC Final Advice. The IESC also indicates in the 2016 IESC
Final Advice that groundwater modelling is appropriate for this stage of the project and is consistent
with industry standards. This is also consistent with my view.
7.4 I believe that the groundwater conditions included in the EPBC Approval and those conditions
already imposed through the CG's Imposed Conditions, the Draft EA conditions and the additional
conditions proposed by the Applicant during the proceedings, provide a high level of protection and
safeguard for all groundwater users.
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8. Expert's statement
8.1 I confirm that:
(a) the factual matters included in this statement are, as far as I know, true;
(b) I have made all enquiries that I consider appropriate;
(c) the opinions stated in this statement are genuinely held by me;
(d) this statement contains reference to all matters I consider significant;
(e) I understand I have a duty to assist the court and that duty overrides any obligation I may
have to any party to these proceedings or any person who is liable for my fees or
expenses and I have complied with that duty;
(f) I have read and understand the rules contained in Part 5 of the Land Court Rules 2000, as
far as they apply to me; and
(g) I have not received or accepted instructions to adopt or reject a particular opinion in
relation to an issue in dispute in these proceedings.
Brian Barnett
20 February 2017
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Schedule 1 - Glossary
2014 IESC Advice the IESC Advice to the DoEE dated 10 April 2014 regarding the New Acland Coal Mine Stage 3 Expansion (Annexure C to the Currell SoE, Document ID: OCA.0021) (Exhibit 435), pages 51-60
2015 IESC Advice the IESC Advice to the DoEE dated 10 December 2015 regarding the New Acland Coal Mine Stage 3 Expansion (Document ID: TMP.0009) (Exhibit 495)
2016 IESC Final Advice IESC final advice with respect to the New Acland Coal Stage 3 Expansion dated 14 December 2016 attached to this statement at Annexure B
AEIS additional information to the EIS (Document ID: EHP.0087 - EHP.0113) (Exhibits 87 - 113)
Applicant's Groundwater Conditions the conditions contained in Annexure A of the Applicant's Reply Submissions
Applicant's Reply Submissions the reply submissions of the Applicant dated and filed 30 September 2016
CG Coordinator-General
CG's Report the report on the EIS and AEIS of the CG dated 19 December 2014 (Document ID: EHP.0016) (Exhibit 16)
DNRM the Queensland Department of Natural Resources and Mines
DoEE Commonwealth Department of the Environment and Energy
EPBC Act Environment Protection and Biodiversity Conservation Act 1999 (Cth)
EPBC Approval the approval for the Expansion issued by the DoEE under the EPBC Act, attached to this statement at Annexure H
EPBC Approval Reasons for Decision the statement of reasons for the EPBC Approval attached to this statement at Annexure I
Expansion New Acland Coal Mine expansion that is the subject of these proceedings
Fault Hydrogeological Investigation Program - Drilling and Testing Report
the report titled "New Acland Stage 3 Project Fault Hydrogeological Investigation Program Drilling and Testing Report" dated 9 January 2017, attached to this statement at Annexure G
Fault Hydrogeological Investigation Program Report the report titled "NAC03 Fault Hydrogeological Investigation Program, October 2016 Status Report" (referred to in the 2016 IESC Final Advice as "SLR, 2016a") dated 24 October 2016, attached to this
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statement at Annexure C
Fault Investigation Site the site of a fault investigation as depicted in Figure 5 of this statement
GMIMP Status Report the report titled "NAC03 Groundwater Monitoring and Impact Management Plan (GMIMP) October 2016 Status Report" (referred to in the 2016 IESC Final Advice as "SLR, 2016b") dated 24 October 2016, attached to this statement at Annexure E
GMMP Groundwater Management and Monitoring Plan
Groundwater Model Update - Phase 1 Completion Report
the report titled "New Acland Stage 3 Project Groundwater Model Update Phase 1 Completion Report (Numerical Model Scoping report)" (referred to in the 2016 IESC Final Advice as "SLR, 2016d") dated 24 October 2016, attached to this statement at Annexure F
IESC Independent Expert Scientific Committee
IESC Chair Conditions Letter the letter from the Chair of the IESC to the DoEE dated 21 December 2016 attached to this statement at Annexure J
Imposed Conditions the conditions listed in Appendix 1 of the CG's Report, imposed by the Queensland Coordinator-General under section 54B of the State Development Public Works Organisation Act 1971 (Cth)
Make Good Status Report the report titled "NAC03 Landholder Make Good October 2016 Status Report" (referred to in the 2016 IESC Final Advice as "SLR, 2016c"), attached to this statement at Annexure D
March 2016 IESC Response the response of the Applicant to the 2015 IESC Advice (Document ID: OCA.0037 (Exhibit 721)
New Groundwater Documents has the meaning given in paragraph 3.9 of this statement
OCAA Oakey Coal Action Alliance
OCAA's Closing Submissions the closing submissions of OCAA dated 13 September 2016
OCAA's IESC Submissions the submissions of OCAA dated 23 January 2017 with respect to the admissibility of the 2016 IESC Final Advice
OWS Office of Water Science located within the DoEE
SLR SLR (Consulting)
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Schedule 2 - Documents listed in 2016 IESC Final Advice
Document referred to in advice Comment
BMT WBM, 2016a. Receiving Environment Monitoring Program for New Acland Mine. Report prepared for New Hope Group: R.B21788.002.00.New_Acland_REMP_Design_Document.docx. February 2016.
And
BMT WBW, 2016b. New Acland Mine Receiving Environment Monitoring Program - Pre-Release Survey 2015. Report for New Hope Group: R.B21788.001.00.prereleaseREMP 2015.docx. February 2016.
These documents relate to surface water issues and are not relevant to this statement
Australian Groundwater and Environmental Consultants (AGE), 2014. Groundwater Model Peer Review New Acland Mine Stage 3. Report for New Acland Coal Pty Ltd. June 2014. (Appendix C of Appendix N, AEIS)
Document ID: EHP.0111, pages 228-251 (Exhibit 111)
Department of Environment and Heritage Protection, 2015. Draft Environmental Authority New Acland Coal Mine. State of Queensland. 14 July 2015.
Document ID: EHP.0015 (Exhibit 15) is the EA dated 14 July 2015
Document ID: EHP.0009 (Exhibit 9) is the Draft EA dated 28 August 2015
Department of State Development, Infrastructure and Planning [DSDIP], 2014. New Acland Coal Mine Stage 3 project. Coordinator-Generals evaluation report on the environmental impact statement. State of Queensland. December 2014.
Document ID: EHP.0016 (Exhibit 16)
New Hope Group, 2016. Response to IESC 2015-073: New Acland Coal Mine Stage 3 (EPBC 2007/3423) Expansion. Submission to Department of the Environment. March 2016.
Document ID: OCA.0037 (Exhibit 721)
New Acland Coal, 2014a. New Acland Coal Stage 3 Project Environmental Assessment documents, EIS. January 2014.
Document ID: EHP.0017-EHP.0086 (Exhibits 17-86)
New Acland Coal, 2014b. New Acland Coal Stage 3 Project Environmental Assessment documents, Additional information to the EIS. August 2014.
Document ID: EHP.0087-EHP.0113 (Exhibits 87-113)
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Annexure A - Letter of instruction
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Level 28, Riparian Plaza 71 Eagle Street Brisbane QLD 4000
GPO Box 9806 Brisbane QLD 4001
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Confidential
Email
Brian Barnett
Jacobs Group (Australia) Pty Ltd
Floor 11, 452 Flinders Street
MELBOURNE VIC 3000
17 January 2017
Dear Brian
New Acland Coal Mine Stage 3 Project
1. Introduction
1.1 We refer to the ongoing Land Court matter involving the New Acland Mine Stage 3 Project (Project).
1.2 On 14 December 2016, the Independent Expert Scientific Committee (IESC) published their final advice regarding the Project (2016 IESC Final Advice).
1.3 In the 2016 IESC Final Advice, t