Grounds 3, 5, 12 and 13
47Boral/Minister submitted in several related grounds of appeal as follows:
3. The Court misconceived its role and function, erred in law and constructively failed to exercise its jurisdiction under the Land and Environment Court Act 1979 and the Environmental Planning and Assessment Act 1979 by failing to determine after trial any of the groundwater and river water quality issues the subject of the contested hearing.
Particulars
a. The Court expressly found and concluded that it would not determine the issues of groundwater and river water quality as:
i. it was not satisfied that the Water Management Plan (WMP) could be categorised as an "adaptive management regime"; and
ii. that consequently there was inadequate information with which to determine those issues;
b. In reasoning as above the Court failed to determine the contested issues in the proceedings.
5. The Court denied the Appellant procedural fairness by failing to consider and evaluate the Appellant's submissions and expert evidence on the contested issues at hearing in the proceedings concerning the potential groundwater and river water quality impacts of the Project.
Particulars
The Court expressly did not engage in this task as it concluded that the WMP was not an "adaptive management regime" and that consequently there was inadequate information with which to determine the issues of groundwater and river water quality.
Ground 12
12. The Court erred in law, in finding that the risk of significant harm due to the Project remained uncertain:
(a) contrary to the evidence;
(b) without considering, evaluating or having any regard to the expert evidence, and in particular to the oral expert evidence given at hearing; and
(c) without providing reasons for rejecting that evidence.
13. The Court erred in law in failing to provide adequate reasons for the decision appealed against, including in the respects particularised below.
Particulars
a. The Court failed to provide adequate reasons, based on an assessment and evaluation of the expert evidence, as to why it concluded that there was a significant risk of significant environmental harm (or uncertainty thereto).
b. The Court failed to provide adequate reasons, based on an assessment and evaluation of the written and oral expert evidence, as to why there was inadequate information with which to determine the issues of groundwater and river water quality.
c. The Court failed to give reasons for rejecting the evidence and the Appellant's submission on a central contested issue between the parties which was whether the groundwater discharge into the Wingecarribee River (as varying from time to time) had any material adverse environmental impact on the Wingecarribee River.
d. The Court failed to give reasons for rejecting the Appellant's submission that there would be no material impact on groundwater drawdown (and aquifer impact) due to the Project as all groundwater experts accepted and agreed that the area and extent of impact would not materially change from that which has already occurred from 85 years of mining at the Berrima Colliery.
e. The Court failed to give reasons for rejecting the expert evidence that the Project would be in compliance with Ecologically Sustainable Development if the conditions agreed between the experts in joint conference were imposed.
f. The Court failed to give reasons, based on an assessment and evaluation of the competing expert evidence in the expert statements of evidence, joint reports and the oral evidence given at hearing, for not concluding that there was a sufficient body of credible evidence to support an approval of the Project by the Court.
g. The Court failed to give reasons for rejecting the submission that the conditions of approval and the WMP, together, could be categorised as an "adaptive management regime", or could otherwise acceptably manage the environmental impacts of the Project.
48These four grounds can be considered together as although expressed differently they are based on the same issue. Boral and the Minister essentially argue that the Commissioners failed to address their respective cases at all but rather focussed exclusively on the case SHCAG presented in closing submissions in finding that because the draft WMP was not an adaptive management plan that was a basis for refusing development consent. Such an approach was impermissible as it did not adjudicate on the issues put to the Court by all the parties about the project's environmental impact or provide reasons in relation to the Appellants' submission concerning that impact. It was necessary to resolve those issues in order to resolve the key issues in the proceedings.
49To understand these grounds an overview of the nature of the parties' statements of contentions, the written and oral submissions to the Commissioners and the expert evidence is required. The detailed contentions identified by SHCAG's SOFC were:
(i)The project was inconsistent with ecologically sustainable development (ESD) principles (par 65).
(ii)The project involves risk of environmental harm to groundwater which is uncertain and not adequately mitigated and the project was therefore not in accordance with ESD's precautionary principle ((b), (c)). Numerous areas of foreseeable environmental risk of harm which are uncertain were identified such as cumulative impact on the groundwater ecosystem, project impact on groundwater levels, calculation of groundwater recharge and impact of mining on aquifer damage induced by dewatering. Mitigation measures proposed were insufficient to prevent the likelihood or severity of harm to the groundwater as there were insufficient groundwater monitoring bores and a lack of performance criteria including trigger levels of groundwater drawdown as part of a groundwater management plan (GMP) (d) (par 66).
(iii)The project will impact permanently on surrounding groundwater systems breaching the principle of intergenerational equity (par 67).
(iv)Loss of groundwater was very likely to critically impact local Groundwater Dependent Ecosystems (GDE). Stygofauna residing in groundwater dependent ecosystems would be impacted by the increased drawdown of groundwater and the introduction of foreign elements from seepage of the Wingecarribee River into the aquifer. The project involves risk of foreseeable environmental harm to GDEs in the groundwater which is uncertain and not adequately mitigated in breach of the precautionary principle (par 68, 69).
(v)Surface water pollution of the Wingecarribee River will occur through discharge of various pollutants. The risk of environmental harm to surface water and hence to aquatic and terrestrial life is uncertain and not adequately mitigated and is not in accordance with the precautionary principle (par 70, 71).
50Boral responded in a detailed SOFC in reply that:
(i)The project was not inconsistent with ESD principles (par 34) responding to SHCAG par 65
(ii)On groundwater impacts, the project's impacts on the quantity of groundwater have been modelled to address scientific uncertainty. While there are some potential risks and associated residual uncertainty, the predicted impacts have not been underestimated so that any impacts will not be significantly greater than predicted. The available data and analysis demonstrates that the current extent of cumulative impacts on groundwater levels due to mining are within 1 km of the mine, predicted dewatering rates are within the measured range over many years, there is no particularly serious risk to groundwater levels and the SHCAG's contention is disproved by the available evidence, the groundwater management plan required by the conditions will include adequate mitigation measures (very lengthy particulars (a) - (y)) (par 35 responding to SHCAG par 66).
(iii)There would be no material loss of groundwater impacting on landowners' groundwater sources (par 36 responding to SHCAG par 67).
(iv)On groundwater biodiversity (par 37 responding to SHCAG par 68, par 38 responding to SHCAG par 69) denies the project will very likely critically impact local GDEs for various particularised reasons ((a) - (h) par 37).
(v)On surface water pollution (par 39 responding to SHCAG par 70), there is adequate and appropriate information to assess the project's impacts on surface water as detailed in particulars (a) - (p) in par 39. Paragraph 40 responding to SHCAG par 71, denies the project involves a risk of environmental harm to surface water which is uncertain and not adequately mitigated, particulars (a) - (h).
51There was reliance on a WMP or its constituent parts such as a GMP as required by condition 31 at 35(d) particular (w) concerning groundwater responding to par 66 of SHCAG, par 36(b) responding to par 67 of SHCAG concerning impact on landowners' groundwater resources, par 37(h) responding to SHCAG par 68 concerning groundwater biodiversity and par 38 responding to par 69 of SHCAG. Paragraph 38 states:
In relation to paragraph 69, the Second Respondent says that the GMP requirements imposed under condition 31 of the Project approval adequately address the requirements of ESD, and its precautionary principle, in relation to possible impact on GDEs. In the alternative, the Second Respondent says that the precautionary principle is not triggered by the Project as there is no threat of serious or irreversible harm to GDEs, nor is there any uncertainty in relation to the nature and scope of the threat of harm to GDEs due to the continued operation of the mine.
52A WMP is also referred to in par 40(b), (d) (the Surface Water Management Plan (SWMP)) and (g) responding to SHCAG's par 71 concerning surface water pollution. The Minister's SOFC adopted Boral's contentions and also submitted that condition 31 was adequate to meet the concerns of SHCAG in its SOFC par 66 and 67, and conditions 29, 30 and 31 met concerns in SHCAG's par 70 and 71.
53The Appellants created a document in tabular form in this appeal headed "The Commissioners' findings on the Second Respondent's submissions and the Minister's submissions and statement of facts and contentions in reply" (Commissioners' findings document) in which nine issues raised in closing submissions are identified as follows:
(1)There is a sufficient body of credible information before the Court enabling the assessment of the impacts of the project (Boral's closing submissions par 14, transcript page 275 lines 5 -15; Minister's closing submissions par 30, transcript page 301 lines 30 - 45, page 303 line 42 to page 305 line 3).
(2)Refusal of this project application in all the circumstances would be a quite disproportionate response to environmental impacts that are addressed in the material before the Court and of which the project approval conditions require investigation, monitoring and management (Boral's closing submissions par 15, transcript, page 290 lines 46-50, 291 lines 1- 9; 298 at lines 15 -20, page 274 lines 34 -50).
(3)The impacts of the continued mining, when considered alongside the existing land features and the significant legacy impacts of past mining carried out over 85 years by multiple operators, are not themselves significant and are best and properly manageable by legally enforceable conditions and the Applicant's chief environmental concern, namely the flow of natural groundwater through the mine into the Wingecarribee River, would occur absent further mining (Boral's closing submissions, par 34(a) and (b), transcript page 270 lines 30-46, page 271 lines 25-39, page 278 lines 33-40, page 287 lines 23-50, page 288 lines 1-4, page 289 lines 6-50, page 290 line 8, and page 296 lines 41-47; Minister's closing submissions par 21 - 36, transcript page 300 lines 33 - 45).
(4)Maximum or very near maximum groundwater drawdown has occurred already, with hydrological equilibrium having been reached and the area and impact of this drawdown unlikely to change with continued mining (Boral's closing submissions, par 34(c), transcript page 275 at lines 45-50 to 276 line 34; Minister's closing submissions par 47, 41 - 45, 52 - 54, transcript page 303 lines 42 - 50).
(5)The downstream concentrations of various minerals in the groundwater (Mn, Ni etc.) are within the relevant ANZECC guideline trigger value (Boral's closing submissions, par 34(e), transcript page 278 at lines 41-50, page 283 lines 25-44; Minister's closing submissions par 56 - 60).
(6)The Applicant's stygofauna expert Dr Remko Leys has confirmed that the project, conditioned with the stygofauna monitoring condition agreed in the Joint Report, would be in line with ESD and that additional mining will be a low risk of impact on stygofauna biodiversity (Boral's closing submissions par 34(h), transcript page 280, lines 21-35; Minister's closing submissions par 55 - 57, transcript page 304 lines 33 - 38).
(7)There is no adverse water quality impact at the site boundary (the mining lease boundary) leading to compliance with the Nor Be guidelines (Boral's closing submissions, par. 34(j), transcript page 282 lines 8-50, page 283 lines 1-24; Minister's closing submissions par 61 - 62, transcript page 303 lines 22 - 33).
(8)There is no likely causal link on the evidence between the future discharge from the mine and the levels of minerals, such as Mn and Ni, in the downstream Wingecarribee River. Ultimately, there was no causal link argued for by Dr Campbell, who now attributes the downstream levels (which are acceptable in any event) to the agitation of minerals in the sediment in the river itself (which were placed there by a variety of sources perhaps over many years or decades) at times of high flow, not to the actual real time discharge from the mine (Boral's closing submissions par 34(k), transcript page 283 lines 25-50 to page 285 lines 1-31; Minister's closing submissions par 59).
(9)Ecotoxicological and stream health analysis reveals that there is good recovery of stream health downstream of the adit discharge, with almost identical SIGNAL scores upstream and downstream, including close to the adit within the mixing zone as close as 250m from the discharge (Boral's closing submissions par 34(l); transcript page 285 line 50 to 288 lines 1-19; Minister's closing submissions par 60, transcript page 304 line 43 to page 305 line 3).
54Seven of these submissions (1, 4, 5, 6, 7, 8, 9) are on topics relating to surface and groundwater impacts and expert evidence in relation to these. Submission 2 is that refusal of the project in all the circumstances was a disproportionate response to the environmental impacts. Submission 3 is that the impacts of continued mining considered alongside existing land features and the significant legacy impacts of past mining carried out over 85 years by multiple operators are not significant. Reference to each issue in the statements of facts and contentions, written submissions, transcript and expert evidence is identified. The final column records that none of the issues (and therefore no findings and reasoning) are referred to in the judgment. In relation to topic 9 concerning ecotoxicological and stream health analysis the document states that:
... there is no specific finding, rather there is a general and incomplete recording at [49] the third bullet point of which records a positive finding based on Anink and Perrens. The last bullet point is not based on any evidence. There is no reasoning and there are no conclusions in the judgment as to why despite this evidence, the Court found at [89] that the proposal may result in significant environmental harm that includes an adverse impact on the Wingecarribee River by discharging pollutants in the water discharged from the mine.
55I was taken to the multiple references to these topics in the written and oral submissions of Boral and the Minister and the evidence of the groundwater, stygofauna and surface water experts where relevant to these topics. The SHCAG did not challenge the contents of the Commissioners' findings document and it argued the subject matter is irrelevant to this appeal. I accept the contents of this document as accurately reflecting the conduct of the matter during the first instance hearing to the extent the document deals with that.