Ground 1
94 The applicant's submissions about the nature and relevant content and processes of the Management Plan for the TWWHA, including the RAA process, are set out at [43]-[60] of its principal written submissions, and the Minister's submissions did not in substance dispute what is in those paragraphs. I accept them. As well as the Management Plan, the regulatory mechanism employed in respect of the use of land in the TWWHA appears to be (relevantly) the grant of a lease or licence under s 48 of the NPRM Act and the potential to cancel that lease or licence under s 51, for - amongst other matters - breach of conditions.
95 The Management Plan purports to adhere to the requirements of s 321 and s 322 of the EPBC Act, concerning the management of World Heritage properties. Section 321 provides:
321 Co‑operating to prepare and implement plans
(1) This section applies in relation to a property that is included in the World Heritage List.
(2) The Commonwealth must use its best endeavours to ensure a plan for managing the property in a way that is not inconsistent with Australia's obligations under the World Heritage Convention or the Australian World Heritage management principles is prepared and implemented in co‑operation with the State or Territory.
Note: The Commonwealth and the State or Territory could make a bilateral agreement adopting the plan and providing for its implementation.
(3) Subsection (2) does not apply in relation to so much of a property as is in the Great Barrier Reef Marine Park.
Note: A zoning plan must be prepared under the Great Barrier Reef Marine Park Act 1975 for areas that are part of the Great Barrier Reef Marine Park. In preparing a zoning plan, regard must be had to the Australian World Heritage management principles.
96 Thus, one of the purposes of the TWWHA Management Plan is the discharge of the Commonwealth's obligation under this provision, and in that discharge, compliance with its international obligations under the World Heritage Convention. The Plan states as much in the executive summary. These purposes are also reflected in Sch 5 of the Regulations. However, there is no suggestion by the terms of s 321 and s 322 of the EPBC Act that the existence of a management plan in World Heritage areas, nor an actor's compliance with it, is a method of avoiding, or disengaging, the controlled action provisions in Pt 8.
97 For the purposes of ground 1, the key point is that the functions and objectives of a management plan such as one made under ss 19-28 of the NPRM Act, and taking into account the lease and licence provisions in s 48, are obviously much broader.
98 As the brief to the delegate stated, and consistently with cl 3.02 of Sch 5 to the Regulations, the RAA process required an EPBC Act referral. It did not, in its terms, purport to be a substitute for the EPBC Act process: quite the contrary, it required a proponent such as Wild Drake to seek and obtain statutory permission to take an action under the EPBC Act. That is a critical fact which should not be overlooked: the RAA process did not purport to be of the same character as a bilaterally accredited process, or any other substitute process for which the EPBC Act provides and for which it accordingly provides an exemption. The brief also stated that the RAA process "will be finalised after the EPBC Act referral decision, and assessment if required has been completed…".
99 In my opinion the brief, adopted by the delegate as his reasons, made it clear that the delegate believed the action could be taken without a significant impact on any of the identified matters of national environmental significance only if it was carried out in a particular manner. Indeed, in my opinion the brief, standing as the delegate's reasons, indicated that the delegate's belief incorporated a number of aspects about how the action needed to be carried out, in order to avoid any likelihood of significant impact. I note that unlike Triabunna, this is not a situation where the delegate made any finding about actual significant impact and then how to avoid it. This is a decision centring on the "likelihood" of significant impact, rather than the formation of a view there would be such an impact.
100 The following matters have contributed to the finding of fact I make about how the delegate's reasons (ie the brief) should be interpreted.
101 Despite the conduct of the RAA, and the imposition of a series of conditions on Wild Drake through that process, the Department sought further information on the delegate's behalf from Wild Drake. That information was set out in a letter which was contained in Attachment B1 to the delegate's brief, and relevantly stated:
Our initial examination of your referral indicates that there is insufficient information to allow us to consider all the relevant issues. To assist the Department in making a decision on the referral, please provide the following information:
• identification of the values of the Tasmanian Wilderness World Heritage Area that may be impacted by the proposed action;
• management measures proposed to avoid and mitigate impacts on the identified values, including increased fire risk;
• survey information for the helipad site;
• location of proposed walking paths from the helipad to the boat launch;
• the system proposed to manage waste (including waste water and sewage) on Halls Island;
• measures to be imposed under local and state government approvals; and
• conditions attached to the current Halls Island leasehold.
102 These were all material issues, most of which went directly to the consideration of any adverse impacts on the applicable Pt 3 matters (see s 75(2)).
103 The result of this request was, amongst other material, the submission by Wild Drake of the PMEMP for the proposed action. In the introduction, the PMEMP described its overall purpose as:
… to ensure that the impact and avoidance strategies and procedures prescribed in the Halls Island Consideration of MNES, potential impacts, avoidance and mitigation measures are identified, encapsulated and implemented within the proposed activities and actions.
104 The Halls Island Consideration of MNES, potential impacts, avoidance and mitigation measures was another document provided by Wild Drake in response to the Department's request for further information. It is a document of substantial length, which as part of its title indicated its purpose was to address "potential impacts, avoidance and mitigation measures". The document identified each relevant World Heritage value, and other matters of national environmental significance (such as the presence of threatened flora and fauna) and in respect of each, set out the potential impacts, the level of risk, the consequences of those potential impacts, the measures which would be taken to manage or avoid the potential impacts, and the contended risk and likelihood of significant impact if those measures were taken. Although the extracts are lengthy, it is necessary to set out three examples, so that the detail can be understood, as it is the method which these extracts reveal, and the delegate's acceptance of what was in this document, that informs how the applicant contends the delegate misunderstood his task under s 75(1), for the purposes of ground 1. The delegate's acceptance of these measures, in the terms they are expressed, is also important to my conclusion that the delegate did, in fact, form a belief about the "particular manner" in which the action would be carried out.
105 The first example relates to one of the TWWHA's World Heritage values:
Value: Criteria ix; Values representing significant ongoing geological processes, biological evolution and man's interaction with his natural environment
Matter: Impacts to relatively undisturbed landscape.
Potential impacts (to establish the likelihood of a significant impact on MNES): Disturbance from infrastructure and on-island use.
Likelihood Low. Built-infrastructure will be located in an area with existing human-habitation / structures and use (modified apparent naturalness).
Consequence: Disturbance to the relatively undisturbed landscape.
Risk: Low.
Mitigation and management measures
Existing measures (RAA, lease and licence conditions) to be fully adopted
• RAA Step 6 Activity controls # 4.1.3.1, 4.1.3.2, 4.1.4.1, 4.1.5.1, 4.1.8.1, 4.2.3.3, 4.2.3.4, 4.2.5.1 and implement all RAA Step 8 Conditions
1) 4.1.3.1: (Geoconservation) Camp will be installed using hand-tools / battery operated tools only. Minimal ground disturbance, no excavations or changes to water-courses.
2) 4.1.3.2: (Western Tasmania Blanket Bogs) Sites are avoided. Any interaction with sites will involve minimal ground disturbance, perforated decking and boardwalking.
3) 4.1.4.1: (Landscape & Viewfield) Sympathetic building material selection, no reflective materials, muted bush tones.
4) 4.1.5.1: (Wilderness and wild rivers, NWI (National Wilderness Inventory) 14+) Restrict maximum group sizes of 6 customers, restrict number of commercial trips to 30 per year. Sympathetic building designs and scale. Adhere to strict flight path and impact minimisation prescriptions in Attachment 10.
5) 4.1.8.1: (Water quality / CFEV (Conservation Freshwater Ecosystem Values) Values) Installation of complete-capture sewage and greywater pods. Greywater will be back-loaded with each trip, for disposal outside of the TWWHA. Sewage will be collected annually in pods and emptied off-site.
6) 4.2.3.3: (Recreational values, established uses) Minimise helicopter use, use helicopter route as described which avoids recorded & formal walking routes, and all significant recreational fishing waters. Restrict annual trip (booking) numbers during peak season (Oct-May) to 25 trips. Adhere to impact minimisation prescriptions in Attachment 10.
• Step 8 Conditions:
7) (Wilderness Character) Prepare and comply with an Operations Plan to include: 'Fly Neighbourly Advice and identified flight path between Lake St Clair and helipad. Conditions are also to be incorporated into the lease and licence. Adhere to helicopter prescriptions in Attachment 10 to minimise point-impacts.
• Lease and Licence conditions including: 12.4, A2.2(d,l,k,l,m), A2.4(a), A2.5(d), A3.8d(i), A3.8e(l,ii), B1.2(c), B1.2(f), C2.2, C4(A, Bii, Bvii, Bviii, Bix, BxiiC)
8) 12.4: Compliance with management objectives. The Operator must not do anything that is inconsistent with the management objectives (for the purposes of the Act (National Parks and reserves Management Act 2002 Tas)) applicable in respect of the Land.
9) A2.2 (d,l,k,l,m): (l) the design must minimise environmental impacts through:
(i) appropriate footprint design and techniques for the three accommodation huts and the communal kitchen hut, with exact locations and size of huts to be determined in conjunction with the (Tas) Minister;
(ii) the use of a selection of products, materials and methods that reduce or minimise impacts (including in respect of water use, waste production and generation); and
(iii) the development and implementation of actions to ensure that the natural and heritage values of the Park are preserved.
(m) all kitchens, toilets and bathrooms must be designed with a complete capture system. All grey and black waste water must be removed from the Land regularly and disposed of at a Central Highlands Council approved disposal facility.
(k) the design must maximise the retention of existing vegetation and topography.
(i) materials used in external surfaces of the Development must be low-visibility in colour and similar to surrounding vegetation (including a mixture of timber and steel materials in muted bush tones).
(d) the design must protect and present the values of the setting in which the Development is to occur, including in respect of the selection of materials and scale of buildings being complementary and sensitive to the surrounding environment (including vegetation type) with a reduced visual impact.
10) A2.4 (a) l,ii: The Operator must prepare an operations manual detailing the operational practices of the Operator in respect of both the Approved Use and the Licensed Activities (Operations Manual). The Operations Manual must include:
(i) details of the FNA (Fly Neighbourly Advice) and an identified flight path between the identified area of Lake St Clair and the Conservation Area (helipad), including ensuring a standard operating procedure of over-flying potential (*wedge tail eagle) nesting habitat by approximately 1000m altitude where possible (except for the end points of the flight), travelling along the pre-determined route of minimum likelihood of nests and avoiding tight manoeuvres and hovering (including ensuring that any flight path is not within a 1km line of sight of known eagles nests and that any flight does not include any 'view' of the nest);
(ii) impact mitigation measures which are noted in the North Barker Flora and Fauna Assessment dated 21/11/2016, for Riverfly RIV002:
A 2.5(d): Construction Environmental Management Plan
(d) details of how impact mitigation will be managed including the development of site management plan dealing with listed species and communities of the island, risk mitigation measure and supervision
11) A3.8d (l): The Operator must ensure that any helicopter used in connection with the construction and/or operation of the Development:
(i) uses the flight path provided by the Lessor to ensure minimal airtime and minimal impacts on other users of the area;
12) A3.8e (l,ii): (e) Except for emergency situations, helicopters:
(i) must not be operated at frequencies greater than those from time to time approved in writing by the Minister; and
(ii) must operate substantially in accordance with any applicable operations schedule from time to time approved in writing by the (Tas) Minister.
13) B1.2(c,f): B1.2 General Obligations
(c) to comply with all requirements and recommendations of the FNA (as may be amended generally or in respect of the Business only where such amendments are agreed between the parties acting reasonably) at all times during the Term including ensuring the recommended flight paths and altitude requirements are followed at all times when the helicopter is operating (provided that in the event of any inconsistency between the FNA and any requirements of CASA or relevant legislation the requirements of CASA or relevant legislation will take precedence to the extent of the inconsistency);
(f) discourage smoking from occurring on the Land and within the Park generally but in the event smoking occurs the Operator must ensure that appropriate butt storage is provided and all butts are removed from the Land and disposed of appropriately.
14) C2.2: At all times while on a Activity the Operator must use all reasonable endeavours to ensure that the environment and ecology of the Licensed Area is in no way damaged by the Experience Guides and Clients including ensuring all staff and Clients clean, dry and disinfect any waders or equipment prior to accessing the Land and the Licensed Area.
15) C4 (A, Bii, Bvii, Bviii, Bix, BxiiC): C4 Transport Service
(a) The Operator must not operate or use, or arrange for the operation or use of, a helicopter within the Park except in accordance with this clause C4.
(b) The Operator may operate or use, or arrange for the operation or use, of a helicopter within the Park subject to the following provisions:
(ii) ensure that the flight path enclosed at Attachment B 'Flight Paths' is followed at all times;
(vii) complies with the FNA including ensuring a standard operating procedure of over-flying potential nesting habitat by approximately 1000m altitude where possible (except for the end points of the flight), travelling along the pre-determined route of minimum likelihood of nests and avoiding tight manoeuvres and hovering (including ensuring that any flight path is not within a 1km line of sight of known (wedge tailed) eagles nests and that any flight does not include any 'view' of the nest);
(viii) unless otherwise agreed in writing by the (Tas) Minister, helicopters must only land and take-off from the recognised landing pad, the final location to be determined in accordance with Schedule A;
(ix) except for helicopter operations required for the construction of the Development or in respect of emergency situations, helicopters must only be used for supply and servicing runs in respect of a Land or in connection with maintenance of the Operator's Improvements and in accordance with the approved Operations Manual in accordance with clause A2.2;
(xii) except where necessary because of overriding safety considerations, the Operator must ensure that helicopters:
(c) are operated in a manner that minimises noise and disturbance to other users of the Park;
• Additional proponent proposed measures
16) The Standing Camp site will be rested from commercial activities for the period June-September annually (4 months), with the minor allowance of up to 5 commercial trips (20days) during this period, as per RAA approvals.
Risk after mitigation and management measures are in place: Low. Appropriate Standing Camp design and siting ensures that infrastructure does not impact on areas relatively undisturbed landscape. Low volume helicopter use and impact mitigation measures ensure that impacts on other users of the landscape is minimised.
Likelihood of a significant impact: Low - no significant visual or physical impacts from Standing Camp infrastructure, and minimal impacts from associated site usage.
106 The second also relates to a World Heritage value:
Value: Criteria X - Values of the most important and significant habitats where threatened species of plants and animals of outstanding universal value from the point of view of science and conservation still survive.
Matter: Habitats where threatened species of plants and animals of outstanding universal value from the point of view of science and conservation communities' and species of conservation significance still survive (eg: sphagnum peatland, Athrotaxis selaginoides rainforest).
Potential impacts (to establish the likelihood of a significant impact on MNES): Trampling & track formation related to on-island activities and proposed walking routes from helipad to lake edge.
Likelihood: Low-Moderate.
Consequence: Damage to the integrity of susceptible features arising from trampling, track formation and subsequent erosion.
Risk: Moderate.
Mitigation and avoidance measures
Existing measures (RAA, lease and licence conditions) to be fully adopted
• RAA Step 6 Activity controls # 4.1.1.1, 4.1.1.3, 4.1.1.4, 4.1.3.1, 4.1.3.2 and implement all RAA Step 8 Conditions
1) 4.1.1.1: Adopt all mitigation measures prescribed in the avoidance of trampling (on-island) within the Flora and Fauna Assessment:
a. Avoid routes through MSP's, or facilitate passage across MSP's by installing raised, perforated boardwalking. Risk is mitigated.
b. Education and supervision during trips, in relation to avoidance of trampling.
c. Siting of standing camp among ORO or WSU communities.
d. Create visitor exclusion zones, excluding visitors from sensitive communities MSP, RKP and Pherosphaera hookeriana communities (see Site Plan Map).
2) 4.1.1.3: Install raised, perforated boardwalk along area of existing impact.
3) 4.1.1.4: Ensure on-island routes/tracks avoid Pherosphaera hookeriana. Where existing routes pass by this species (near the natural rock landing), use short lengths of boardwalk to ensure clear walking route that avoids plant species. Education and supervision to re-enforce impact mitigation. Utilise no-access areas for visitors, see Site Plan Map including exclusion zones.
4) 4.1.3.1: Camp will be installed using hand tools / battery-operated tools only. Minimal ground disturbance, no excavations or changes to water-courses.
5) 4.1.3.2: Blanket bog sites are avoided.
• Step 8 Conditions:
6) Implement all avoidance and mitigation measures outlined in the Flora and Fauna Assessment; prepare a Construction Environmental Management Plan (CEMP) covering the construction phase, to be approved by the PWS.
7) Through the CEMP, make staff and contractors working on Halls Island aware of the location of threatened plants and threatened native vegetation communities to ensure no inadvertent impact to these natural values.
8) Flag work area to avoid inadvertent disturbance of threatened plants (Pherosphaera hookeriana pines) during construction. Include in CEMP.
9) Locate the Halls Island landing such that these plants do not need to be removed, but if this is not practicable or safe, and any of these threatened pines need to be taken, then a permit to take under the Threatened Species Protection Act 1994 will be required from PCAB prior to any impact.
• Lease and Licence conditions including A2.3, A2.4 (ii), A2.5(d), C2.2
10) A2.4 Operations Manual
(b) The Operator must prepare an operations manual detailing the operational practices of the Operator in respect of both the Approved Use and the Licensed Activities (Operations Manual). The Operations Manual must include:
(ii) impact mitigation measures which are noted in the North Barker Flora and Fauna Assessment dated 21/11/2016, for Riverfly RIV002, including:
(A) avoiding MSP - Sphagnum peatland, RKP - Athrotaxis selaginoides rainforest and Pherosphaera hookeriana locations (the Operator, where necessary, can apply to construct boardwalks over locations not specified in the RAA, which application will be subject to the written consent of the Minister including any necessary further assessment);
(D) using continual education and supervision as part of the overall interpretation and presentation of the Land to ensure minimal impact.
11) A2.5: Construction Environmental Management Plan - The Operator must, before making any application for Development Approval to the Central Highlands Council and/or undertaking any Development Works on the Land prepare a plan ('Construction Environmental Management Plan'), in a form and substance satisfactory to the Minister, to deal with the following matters:
(d) details of how impact mitigation will be managed including the development of site management plan dealing with listed species and communities of the island, risk mitigation measure and supervision;
12) C2.2 Management of the Environment: At all times while on an Activity the Operator must use all reasonable endeavours to ensure that the environment and ecology of the Licensed Area is in no way damaged by the Experience Guides and Clients including ensuring all staff and Clients clean, dry and disinfect any waders or equipment prior to accessing the Land and the Licensed Area.
• Additional proponent proposed measures
13) Additional on-site assessments (30 May 2018) have identified a suitable helicopter landing location (see Helipad Site 2 - Proposed Helipad and access to Halls Island Vegetation Survey 20 May 2018) consisting of naturally exposed bedrock. It is the intention of the proponent to use this area as the Helicopter Landing Site (HLS) without the requirement for added infrastructure (subject to HLS approval from helicopter contractors and meeting applicable CASA regulations). Should infrastructure (formed helipad) be required due to OH&S and/or CASA requirements, a raised perforated deck shall be installed at Site 2, as per Flora and Fauna Assessment impact mitigation prescriptions.
14) Walking route from heli-landing site to the lake-edge shall follow the sclerophyll forest / open plain edge as prescribed in the Flora and Fauna Assessment addendum. When using the route between the western plain edge, and the lake edge, customers and guides shall use fan-out walking techniques to avoid trampling and track formation. Incorporate into CEMP / Operations Manual.
15) Traversing of susceptible poorly drained habitats including sphagnum, blanket bogs and wetlands shall be avoided through the CEMP / Operations Manual
Risk after mitigation and avoidance measures are in place: Low. Activities that could result in trampling are mitigated, and activities that could lead to track formation are avoided.
Likelihood of a significant impact: Negligible-low. Avoidance measures, along with mitigation measures such as education and supervision result in a negligible to low risk of significant impact.
107 The third example relates to one of the key threatened flora species:
Community / species: Alpine Sphagnum bogs and Associated Fens - MSP
Potential impacts (to establish likelihood of a significant impact on MNES): Trampling & track formation related to on-island activities and proposed walking route to and from helipad
Likelihood: Low-moderate.
Consequence: Damage to the integrity of susceptible soils arising from trampling, track formation and subsequent erosion.
Risk: Low-moderate.
Mitigation and avoidance measures
Existing measures (RAA, lease and licence conditions) to be fully adopted
• RAA Step 6 Activity controls # 4.1.1.1, 4.1.1.3, 4.1.3.1, and implement all RAA Step 8 Conditions
1) 4.1.1.1: Adopt all mitigation measures prescribed in the avoidance of trampling (on-island) within the Flora and Fauna assessment:
(a) Avoid routes through MSP's, or facilitate passage across MSP's by installing raised, perforated boardwalking. Risk is mitigated.
(b) Education and supervision during trips, in relation to avoidance of trampling
(c) Siting of standing camp among ORO or WSU communities.
(d) Create visitor exclusion zones, excluding visitors from sensitive communities MSP, RKP and Pherosphaera hookeriana communities (see site map)
2) 4.1.1.3: Install raised, perforated boardwalk along area of existing impact (through MSP)
3) 4.1.3.1: Camp will be installed using hand tools / battery-operated tools only. Minimal ground disturbance, no excavations or changes to water-courses.
• Step 8 Conditions:
4) Implement all avoidance and mitigation measures outlined in the North Barker Flora and Fauna assessment report; prepare a Construction Environmental Management Plan (CEMP) covering the construction phase, to be approved by the PWS.
5) Through the CEMP, make staff and contractors working on Halls Island aware of the location of threatened plants and threatened native vegetation communities to ensure no inadvertent impact to these natural values.
6) Flag work area to avoid inadvertent disturbance of threatened plants (Pherosphaera hookeriana pines) during construction. Include in CEMP.
7) Locate the Halls Island landing such that these plants do not need to be removed, but if this is not practicable or safe, and any of these threatened pines need to be taken, then a permit to take under the Threatened Species Protection Act 1994 will be required from PCAB prior to any impact.
• Lease and Licence conditions including A2.3, A2.4 (ii), A2.5(d), C2.2
8) A2.4 Operations Manual
(a) The Operator must prepare an operations manual detailing the operational practices of the Operator in respect of both the Approved Use and the Licensed Activities (Operations Manual). The Operations Manual must include:
(ii) impact mitigation measures which are noted in the North Barker Flora and Fauna Assessment dated 21/11/2016, for Riverfly RIV002, including:
(A) avoiding MSP - Sphagnum peatland, RKP - Athrotaxis selaginoides rainforest and Pherosphaera hookeriana locations (the Operator, where necessary, can apply to construct boardwalks over locations not specified in the RAA, which application will be subject to the written consent of the Minister including any necessary further assessment);
(D) using continual education and supervision as part of the overall interpretation and presentation of the Land to ensure minimal impact.
9) A2.5: Construction Environmental Management Plan - The Operator must, before making any application for Development Approval to the Central Highlands Council and/or undertaking any Development Works on the Land prepare a plan ('Construction Environmental Management Plan'), in a form and substance satisfactory to the Minister, to deal with the following matters:
(d) details of how impact mitigation will be managed including the development of site management plan dealing with listed species and communities of the island, risk mitigation measure and supervision;
ii C2.2 Management of the Environment: At all times while on an Activity the Operator must use all reasonable endeavours to ensure that the environment and ecology of the Licensed Area is in no way damaged by the Experience Guides and Clients including ensuring all staff and Clients clean, dry and disinfect any waders or equipment prior to accessing the Land and the Licensed Area.
• Additional proponent proposed measures
10) Additional on-site assessments (30 May 2018) have identified a suitable helicopter landing location (see Helipad Site 2 - Proposed Helipad and access to Halls Island Vegetation Survey 20 May 2018) consisting of naturally exposed bedrock within a HHE (Eastern alpine heathland) community. It is the intention of the proponent to use this area as the HLS without the requirement for added infrastructure (subject to HLS approval from helicopter contractors and meeting applicable CASA regulations). Should infrastructure (formed helipad) be required due to OH&S and/or CASA requirements, a raised perforated deck shall be installed at Site 2, as per Flora and Fauna Assessment impact mitigation prescriptions.
11) Walking route from heli-landing site to the lake-edge shall follow the sclerophyll forest / open plain edge as prescribed in the Flora and Fauna Assessment addendum. When using the route between the western plain edge, and the lake edge, customers and guides shall use fan-out walking techniques to avoid trampling and track formation. Incorporate into CEMP / Operations Manual.
12) Traversing of susceptible poorly drained habitats including sphagnum, blanket bogs and wetlands shall be avoided through the CEMP / Operations Manual
Risk after mitigation and avoidance measures are in place: Low. Activities that could result in trampling are mitigated, and activities that could lead to track formation are avoided.
Likelihood of a significant impact: Negligible-low. Avoidance measures, along with mitigation measures such as education and supervision result in a negligible to low risk of significant impact
108 The PMEMP itself contained a series of "subplans" to address potential impacts from aspects of the action. For example, under the topic of "construction", the subplan described its objective in the following terms:
The objective of this plan is to ensure that all impact avoidance and mitigation measures relating to MNES are identified and implemented prior to the commencement of construction.
109 The PMEMP then went sequentially through a number of other areas of potential impact (eg weed and hygiene, Indigenous heritage, species and communities of significance, fire). For "species and communities of significance", the relevant subplan stated the objective was:
… to ensure that all risk related to the proposed activities are avoided, or mitigated.
110 Taking the threatened ecological community of Alpine Sphagnum Bogs and Associated Fens as an example, the subplan cross-referenced back to earlier sections of the PMEMP which set out "mitigation and avoidance measures" for trampling and track formation (being one of the primary potential impacts for this species). That earlier part of the PMEMP stated:
2.3 Trampling and Track formation avoidance
To ensure that trampling, track formation and general disturbance of MNES species and communities is avoided and mitigated, the following measures will be fully adopted for use during the construction process:
(a) Avoid routes through MSP's, or facilitate passage across MSP's by installing raised, perforated boardwalking. Risk is mitigated.
(b) Education and supervision during trips, in relation to avoidance of trampling
(c) Siting of standing camp among ORO or WSU communities.
(d) Create visitor exclusion zones, excluding visitors from sensitive communities MSP, RKP and Pherosphaera hookeriana communities (see site map)
(e) Install raised, perforated boardwalk along area of existing impact (MSP community south of Halls Hut)
(f) Ensure on-island routes/tracks avoid Pherosphaera hookeriana. Where existing routes pass this species (eg: near the natural rock landing), use short lengths of boardwalk or similar appropriate mechanisms to ensure a clear walking route that avoids the plant species. Education and supervision to re-enforce impact mitigation. Utilise no-access areas for visitors, see Halls Island Preliminary Design Plan for Site Plan.
(g) Camp will be installed using hand tools / battery-operated tools only. Minimal ground disturbance, no excavations or changes to water-courses. A small four-stroke generator may be used during the construction process to charge electric tools. This shall be located on the ORO terrain to minimise risk of fire etc.
(h) A Construction Environment Management Plan (CEMP) shall be prepared in accordance with the current RAA and Lease requirements, and will ensure that staff and contractors working on Halls Island aware of the location of threatened plants and threatened native vegetation communities to ensure no inadvertent impact to these natural values.
(i) Flag work area to avoid inadvertent disturbance of threatened plants (Pherosphaera hookeriana pines) during construction. Include in CEMP.
(j) Locate the Halls Island landing such that threatened plants (Pherosphaera hookeriana pines) do not need to be removed. If this is not practicable or safe, and any of these threatened pines need to be taken, then a permit to take under the Threatened Species Protection Act 1994 will be required from PCAB prior to any impact.
111 The PMEMP and its associated documents, along with the referral, were considered by the Department's Heritage Branch. The delegate was informed in the brief at certain points of the view of the Heritage Branch. For example, in the conclusion of the section of the brief titled "World Heritage properties", the delegate was advised that:
The Heritage Branch concludes that if the proposed avoidance, mitigation and management measures are implemented and adhered to, impacts to cultural heritage values, view fields and sites of exceptional natural beauty associated with the TWWHA, and impacts associated with trampling, fire, and the introduction of pests, weeds and pathogens, should be effectively mitigated.
112 The applicant submitted:
The Brief's authors approached the s 75(1) question on the assumption that the Proponent would adopt the mitigation measures proposed in the PMEMP. In other words, they considered impacts as mitigated by the proposed measures, rather than considering the likely adverse impacts without mitigation.
(Original emphasis.)
113 I accept that submission. It is apparent from the extracts above that the approach Wild Drake was, I infer, advised and encouraged by the Department to take to its referral was to put forward a case based on how any likely adverse impacts on matters of national environmental significance would be mitigated or avoided. The objective was to present a complete picture of sufficient mitigation and avoidance measures so as to persuade the delegate there was no likely significant or adverse impact on any matter of national environmental significance, if those mitigation and avoidance measures were implemented in the taking of the action. The delegate's discharge of the statutory task in s 75, I am persuaded, was not undertaken by consideration of the action alone - taking any of the descriptions of the action which I have set out earlier in these reasons. It was undertaken by consideration of the particular manner in which the action would be carried out, and the large and complex suite of mitigation and avoidance measures which Wild Drake proposed, many of which had also been proposed and accepted (at least for the purposes of "draft approval", as I note below) under the State's RAA process.
114 On the facts as they were before the delegate, the RAA process was incomplete and only "draft approval" had been received for "stage one" (the referral before the delegate). As I have already noted, on the facts before the delegate, Wild Drake was required by the RAA process to refer the proposed action under the EPBC Act. It could therefore not have been used as an assessment process if the action had been designated as a controlled action. Yet it was used to avoid a controlled action designation.
115 The Department treated the RAA as a substitute assessment process, and the delegate did the same by adopting the Department's reasoning. A clear example of this relates to the consideration of potential impacts on Indigenous heritage, and how they were dealt with in the brief. After referring to concerns expressed by the AHC about the "cultural interpretation site visits" Wild Drake proposed to undertake in the future, the brief stated:
The cultural site visits referred to by the AHC are those that form part of the stage 2 proposal, are not part of this referral and have not been approved to proceed in the PWS RAA.
116 That is a clear example of the Department and the delegate treating the non-statutory, State-based RAA process as the de facto assessment process. The scheme of the EPBC Act does not contemplate that will occur, outside the methods (such as bilateral agreements) for which it provides.
117 The substantive reasoning aspects of the brief bear out this characterisation of the delegate's approach. In relation to the Tasmanian Wedge-tailed eagle, the brief identified two features under the heading "Avoidance and mitigation measures". First, what the PWS had identified as "management measures" (not circling around or hovering near eagles' nests or potential nests; to fly as highly, swiftly and directly over the nests as possible during breeding season (July-January); and to avoid flying within 1,000 m of the nests, horizontally or vertically, particularly from July-January)), as well as a voluntary code of practice developed by the PWS called "Fly Neighbourly Advice". Second, undertakings given by Wild Drake itself about "additional measures" to "further avoid disturbance impacts": namely, no flights within a 1 km line-of-sight of known eagles' nests, and that eagles observed in operational areas will be avoided; helicopter flights will not include a "viewing" of the nests; and that Wild Drake will adopt the flight route as prescribed in the "Wedge-Tailed Eagle Assessment" provided with Wild Drake's referral information, being a route that avoids interactions with known nesting sites and utilises an area with a low probability of eagle nests.
118 Relevantly to the grounds of review, a similar approach was taken in respect of the Alpine Sphagnum Bogs and Associated Fens threatened ecological community, and to the World Heritage cultural and natural values which were to be protected.
119 In my opinion, and save for what I set out at [129]-[130] below, the approach taken by the delegate would have surrendered the statutory task, and control of the taking of the action, to an incomplete, non-statutory State process, outside the EPBC Act. It would not have been the task contemplated by s 75; it would have been a different task, and one not authorised by the EPBC Act.
120 As the applicant submitted in reply, the delegate's decision meant that s 12(2)(c) and s 19(3) of the EPBC Act were engaged and Wild Drake was not exposed to injunctive or other procedures to enforce compliance with the prohibitions in Pt 3. Those prohibitions had been disengaged by the s 75 decision. Taking some hypothetical examples, the applicant submitted Wild Drake could thereby decide to vary the flight path of the helicopters, including flying lower (which may significantly impact any Wedge-tailed eagles in the vicinity), or might decide to conduct more than the 30 permitted visits per year (which may significantly impact on the wilderness values of the area), and the s 75 decision would render such changes, and such conduct, unregulated by the EPBC Act. In contrast, if the action had been a controlled action, and the measures proposed by Wild Drake, and set out in the RAA, had been imposed as conditions under s 134 of the EPBC Act, the Minister and the Department would have retained an ability to monitor and regulate any such changes and conduct. That ability was surrendered.
121 The Minister submitted at [32] of her principal written submissions, in a theme which ran throughout those submissions, that:
An action that was taken without the mitigation measures which were considered as part of the action that was the subject of the referral would be at risk of being characterised as different to the action that was the subject of the controlled action decision and be liable to enforcement action under a provision of Part 3 of the EPBC Act. In those circumstances, the Minister could also potentially call the action in under s 70 of the EPBC Act.
122 Of course, by this time, the conduct may have occurred and any adverse impacts may be too late to remedy. It is insufficient to point to possible remedial powers or the need for another round of allegations and counter allegations about whether the prohibitions in Pt 3 have been contravened. That is not how the EPBC Act is intended to operate. It is not intended to facilitate granular arguments to be made after potentially damaging conduct has occurred about whether an action is the same action or a different one to that which was approved. The fact that in a situation such as this, such granular arguments would be occurring in the context of a decision under s 75 that the action was not a controlled action at all would make the matter extremely difficult and complicated. That is not a workable solution to the problem which has arisen due to the approach taken by the Department and the delegate.
123 Further, the Minister's reliance on the fact that other State-based approvals were required (eg under the Land Use Planning and Approvals Act 1993 (Tas)) before the action could be taken by Wild Drake does not ameliorate the situation. In several respects, the EPBC Act contemplates (and requires) coordination between State and Commonwealth assessment and approval processes: see Tarkine National Coalition Inc v Minister for the Environment [2015] FCAFC 89; 233 FCR 254 [3]-[17], [50] and [57]-[58]. The conditions power also expressly contemplates such co-ordination: see ss 134(3)(c), (3C) and (4)(a).
124 A further factor which supports this approach is the focus of the assessment processes in Div 3 of Pt 8, and of the decision-making requirements in Pt 9 (especially s 131A) on public participation and comment. Some of the assessment processes available under Div 3 of Pt 8 involve high degrees of public participation, such as an environmental impact statement or a public inquiry. The applicant submitted in reply:
The purposes of the Act are informed by the treaty obligations to which it gives effect, including (relevantly to the present case) articles 4 and 5 of the World Heritage Convention and articles 8 and 14 of the Biodiversity Convention. Article 14(1) of the Biodiversity Convention requires Australia, as far as possible and as appropriate, to "[i]ntroduce appropriate procedures requiring environmental impact assessment of its proposed projects that are likely to have significant adverse effects on biological diversity with a view to avoiding or minimizing such effects and, where appropriate, allow for public participation in such procedures". Parts 5, 8 and 9 of the Act, and s 75(1), are integral components of the means by which Parliament has chosen to give effect to that obligation.
125 I accept that submission. The EPBC Act intends there to be a level of public participation. Its subject-matter is the protection and conservation of matters of national environmental significance. Their protection is a matter in which the Australian community has an interest, a fact the legislative scheme recognises.
126 The Regulations do require a proponent to supply information about mitigation measures in its referral, and although public submissions were invited (and were made) at the s 75 stage in respect of Wild Drake's referral, what is not intended by the scheme is that a de facto assessment process be conducted by the Department, in negotiation with a proponent and out of public view. Subject to the power in s 77A, what is being assessed under the statutory task in s 75 is the adverse impacts of the action, not the adverse impacts of the action once all avoidance and mitigation measures have been applied. Any other approach deprives the public of the participation the World Heritage Convention contemplates will be applied to the protection and conservation of World Heritage values in listed properties.
127 At [79] of its principal written submissions, the applicant contended (omitting footnotes):
The protective purposes of the Act are undermined if mitigation measures can be taken into account under s 75(1) as to whether there are likely to be significant impacts. If the Delegate's approach were appropriate, it would not make sense to have a bilateral agreement as a substitute for assessing environmental impacts, or to contemplate the Commonwealth approval picking up State conditions. Instead, the State could assess the impacts and impose conditions under applicable State legislation, and the Minister could then consider whether the impacts, as assessed and then controlled under the State legislation, were likely to be significant impacts.
(Original emphasis.)
128 There is force in this submission. There is a sense that the Department's approach, including its communications with the proponent prior to the recommendation made to the delegate, was not focussed on assessing the impacts of the action as it was outlined, but rather on discussing with the proponent what mitigation or avoidance measures might be taken so as to reduce the level of potential adverse impacts. As a pathway towards a component decision under s 77A, or as part of considering what kind of assessment process under Pts 8 or 9 should be undertaken, that process may well be legitimate and consistent with the scheme of the EPBC Act. If the Department's approach goes beyond this, then I agree with the applicant it can tend to frustrate the entire scheme of the EPBC Act. While administrative negotiations might avoid a longer, more complex, public and perhaps more resource intensive assessment process, it is not a course of conduct which the EPBC Act contemplates as an entire substitute for use of the mechanisms for which the Act provides so as to regulate the taking of an action. Through a complex and prescriptive piece of legislation, Parliament has identified which substitute assessment and regulatory processes can be applied to the taking of an action which may engage Pt 3 of the EPBC Act. It has done so with precision. Outside those processes, what is available to the decision-maker (not the Department) is a decision under s 75 that the matter is a controlled action and the imposition of regulatory control through that process, or a component decision under s 77A.
129 However, I do not ultimately reach the conclusion on ground 1 which might be suggested from what I have set out above. That is because the appropriate way to interpret the brief, consistently with the legislative scheme, is to see the decision through the lens of s 77A, as a component decision or decisions. Consistently with at least some aspects of the Minister's supplementary written submissions, I have concluded that what the delegate was in reality deciding was that he believed the action would not be likely to have a significant impact if carried out in a certain manner. In its outcome in terms of the content of the s 77 notice, the decision did not reflect this belief, and that is why ground 2 succeeds.
130 There will be a point beyond which the approach taken by the Department (and, I infer, an approach the Department encouraged the proponent to take) must inevitably result in a decision under s 75 being wholly set aside. That will occur where it is not possible to find that the decision-maker "believed" there would be no significant impact or no likelihood of significant impact because the action would be carried out in a particular manner. After some reflection, I have concluded that the better characterisation of what the delegate did is the one I have set out at [129]. I do not consider the delegate adopted an approach which entirely frustrated or avoided the statutory scheme.