Grounds 4, 5 and 6
42 These three grounds assert much the same thing. Ground 4 is that the impugned conditions in substance and effect constitute an assessment and/or provide for an approval in respect of the action. Ground 5 is that the conditions are for the purpose of predicting the impact of the action on the marine area. Ground 6 is that the conditions constitute an assessment of the action because the completion of the modelling is essential to achieving an understanding of the impact of the action.
43 In order to deal with these grounds it is necessary to examine the Minister's reasons for granting approval subject to conditions. Under the heading The Commonwealth marine environment (pars 49 to 56) the Minister made a number of findings and observations:
· he found that the Commonwealth marine environment may be affected by effluent discharge into Bass Strait from the marine outfall proposed for the mill, which would be situated 2.7 km offshore;
· he noted that, based on the available evidence, the Department had not identified any likely significant impacts on the marine environment in Commonwealth waters;
· he noted that the Chief Scientist's report stated that, based on current international experience, an Elemental Chlorine Free (ECF) mill incorporating best available technology should enable an effluent composition to be achieved that meets best practice Australian and international water quality standards outside the initial mixing zone, and that implementation of these technologies will achieve an effluent composition that is substantially better than those in the State permit conditions;
· he noted that notwithstanding the Department's and the Chief Scientist's opinions, both advised him that monitoring of pollutant levels in Tasmanian waters would be prudent to ensure no indirect adverse impacts on Commonwealth's waters;
· he noted advice from the Department and the Chief Scientist that there is no analogous situation in terms of a new ECF mill discharging effluent into a marine environment which has not previously been exposed to effluents of this nature. Dioxin levels from overseas mills into which effluent has been discharged over many years are much higher than could be expected to result from the operation of the proposed mill, a greenfields ECF mill;
· he noted the advice of the Chief Scientist that residual risk posed by the lack of analogous situations and doubts about the Gunns modelling could be managed by appropriate monitoring;
· he found that, given the absence of a reliable model for predicting possible sediment and biota concentrations, the lack of effluent and sediment field data from comparable greenfields ECF mills and the different possible interpretations of the hydrodynamic model used by Gunns, it was advisable that competent monitoring programs be put in place to provide early warning of any unexpected trends and allow adequate opportunity to correct them;
· he found that Gunns could be required to obtain effluent samples from overseas pulp mills using technologies similar to that proposed, and conduct chemical analyses and whole effluent toxicity testing to identify the key contaminants and their concentrations and the effluent dilutions needed in the mixing zone for the mill;
· he found that Gunns could be required to undertake additional modelling in relation to the fate of effluent, as part of the EIMP, prior to the commencement of commissioning of the mill; and
· he concluded that if these measures were enforced through conditions of approval, the action would not have a significant impact on the Commonwealth marine environment.
44 Under the heading Environmental Impact Management Plan, the Minister
· found that, as recommended by the Chief Scientist, an efficient, effective and transparent means of ensuring minimal adverse impacts on matters of national environmental significance would be to require that, as part of the approval conditions, Gunns develop an EIMP for his approval;
· found that it should be an operational objective of the mill, reflected in the EIMP, that trigger points and maximum limits in relation to effluent discharge not be reached;
· said it was his expectation, based on the advice of the Chief Scientist and the Department, that the mill will operate at levels of emissions significantly below the trigger points he was proposing to require;
· notwithstanding the foregoing, considered that a precautionary approach would be appropriate where effluent discharges must be monitored on a daily basis with remedial action being required should trigger levels be exceeded in any one month.
45 Under the heading Reasons for decision the Minister:
· in deciding whether or not to approve the taking of the proposed action, said he had taken into account (amongst other matters) the principles of ecologically sustainable development (s 136(2)(a)) and the precautionary principle (s 391);
· considered his proposed decision would be consistent with the principles of ecologically sustainable development because of the strict conditions he was contemplating imposing in accordance with the precautionary principle;
· concluded that any lack of certainty related to the potential impacts of the effluent discharge would be satisfactorily addressed by conditions that restrict the discharge of pollutants to prescribed levels, impose strict monitoring of the effluent and the receiving environment, and adopt trigger points and maximum limits which, if exceeded or reached, require the application of remedial management responses in a timely manner to avoid adverse impacts; and
· concluded, in light of his findings, that the likely impacts of the action on the Commonwealth marine area could be prevented or mitigated by attaching conditions to an approval, and that the action carried out in accordance with these conditions would not have significant impact on Commonwealth marine areas.
46 The precautionary principle to which the Minister referred at [85] of his reasons is a matter he is required by s 391 to take into account in making a decision under s 133 "to the extent he or she can do so consistently with the other provisions" of the Act. The principle is that:
lack of full scientific certainty should not be used as a reason for postponing a measure to prevent degradation of the environment where there are threats of serious or irreversible environmental damage.
The precautionary principle was to have featured more prominently in the appeal. However the ground asserting that the Minister had failed to apply it was not pressed.
47 It is apparent from the Minister's reasons that the impugned conditions were not imposed so as to enable him to assess the environmental impact of the proposed action or for the purpose of predicting that impact. Although on the evidence no significant impacts were likely, the conditions were designed to deal with a residual risk from unexpected trends or events, and were imposed in accordance with the precautionary principle for the purpose of guarding against them by resort to monitoring and management.
48 The Minister recorded the Chief Scientist's advice that the residual risks posed by the lack of analogous situations and doubts about the modelling undertaken by Gunns could be "managed by appropriate monitoring", including the fall‑back "management option" of tertiary treatment. The Minister accepted that advice. Part 3 of the Chief Scientist's report is headed Framework for Best Practice Management of Environmental Impacts. After referring to the residual risks mentioned above, the Chief Scientist said that the Panel found that these risks and associated uncertainties should be able to be satisfactorily managed through an EIMP. Among the core components of such a plan recommended by the Panel were the design and implementation of an appropriate monitoring program and identification by Gunns of specific remedial management responses to be undertaken if trigger point levels were exceeded. The report stated that the EIMP should specify management responses, including potential changes to the mill processes and operation that will be undertaken if further studies to reduce current uncertainty around environmental risk and impact result in "unacceptable increases in the assessed risk to Commonwealth environmental assets".
49 The Chief Scientist and the Panel provided what they called a "framework" for best practice "management of environmental impacts". They were not dealing with the assessment of impacts. They regarded the Department as having made that assessment in its draft approval decision. They were concerned with managing unacceptable increases in that assessed risk.
50 Given that the Minister adopted the Chief Scientist's recommendation, describing it as advice that the residual risks could be managed by appropriate monitoring, it is clear that he intended the conditions he imposed to constitute the management of the residual risks or any unacceptable increases in the assessed risks.
51 The appellant submitted that conditions 34, 35 and 38 cannot be regarded as actually managing impacts. That may be so, but in our view they are part of a plan for managing the residual risks to which the Minister and the Chief Scientist referred. Thus, condition 34 requires Gunns to obtain effluent samples from overseas pulp mills already using technologies similar to that proposed and perform various tests to identify the key contaminants and their concentrations. One of the residual risks identified by the Chief Scientist arose because of the "lack of analogous situations". Condition 34 can thus be seen to be part of a management process directed at ascertaining more information about analogous situations so as to become better informed about unlikely but possible risks.
52 Condition 35 requires Gunns to undertake laboratory studies to assess the likely settling and flocculation properties of fine particulate materials in effluent from analogous mills (equivalent effluent). This condition is thus of the same character as condition 34. Further, it is a study to reduce current uncertainty around environmental risk which, though not likely, could result in unacceptable increases in the assessed risk.
53 Condition 38 is concerned with additional modelling in relation to the fate of effluent. Like condition 35, this condition is concerned to reduce current uncertainty around environmental risk. In particular, it is directed to the residual risks posed by doubts about the modelling undertaken by Gunns. The Chief Scientist thought this risk could be managed by appropriate monitoring. The matters to be covered by the monitoring that are listed in the condition are those that appear in par 2.4.1.6 of the Chief Scientist's report. It is plain that he regarded the material that became the condition as part of the management of the risk identified. The Minister accepted the Chief Scientist's advice that residual risks posed by doubts about Gunns' modelling could be managed by appropriate monitoring, informed by a revised hydrodynamic and sediment transport model: par 53. In par 54 the Minister found that in view of, amongst other things, the absence of a reliable model for predicting possible sediment and biota concentration and the different possible interpretations of Gunns' model, it was advisable that competent monitoring programs be put in place to provide early warning of any unexpected trends and allow adequate opportunity to correct them.
54 It is also apparent from the Minister's reasons that the impugned conditions do not constitute a separate approval process. The approval under s 133(1) was accompanied by the conditions attached to it. We do not accept the appellant's contention that s 134 conditions are "subordinate" to the approval. The approval and the conditions came into being uno flatu. Sections 134 and 136 make clear that a consideration of what, if any, conditions are to be imposed will be an integral part of the decision to approve. The Act speaks of a condition being attached to an approval. But it is clear that there are not two different things - an approval and a condition. Rather, when a condition is attached to an approval, there is a conditional approval or an approval subject to conditions.
55 At first instance much attention was given to whether, when the Minister gave his approval subject to conditions, he believed he had enough information to make an informed decision, or in fact had sufficient information for that purpose. We are uncertain whether these matters were pursued on the appeal. On the one hand the appellant, in written submissions, asserted that a decision under s 133(1) is "predicated on the Minister having a detailed understanding of the environmental impact on each matter protected by a controlling provision", and that absent that knowledge, the precautionary principle applies to constrain him granting approval. On the other hand, elsewhere the appellant asserted that its attack on the impugned provisions does not depend on the sufficiency of the evidence before the Minister or "the degree of certainty that attended his state of knowledge".
56 For the avoidance of doubt, if the former of the two apparently inconsistent assertions represents the applicant's position, we should say that we agree with what the primary judge said about the claim that the Minister lacked the required degree of certainty he was required to have as a precondition to the exercise of his powers under s 134. See [18] above. We also agree with his Honour's conclusion that the Minister in fact had sufficient information to enable him to conclude that the likely impact of the discharge of effluent into the marine environment could be prevented or mitigated by imposing conditions which imposed limits, based on overseas experience, on the concentration and volume of toxic materials being discharged. See [20] above. We also agree with his Honour's rejection (at [52] of his reasons) of the submission that the Minister's insistence on the EIMP process itself demonstrated that he lacked sufficient information to make an informed decision to approve the action.