Consideration
62At the conclusion of the evidence the parties were in agreement that it was appropriate for the EPL to be transferred to Always, subject to conditions. The central dispute as to the conditions that should be imposed relates to whether Always should be permitted to receive waste while it reduces the stockpiles to the agreed height of 3m and removes the asbestos stockpiles; whether there should be a condition limiting the stockpiles to a specified volume; and the amount of the financial assurance required.
63Chapter 3 of the POEO Act contains the provisions for EPLs, including in s55 the power to transfer an EPL. As noted above, Part 3.5 contains particular conditions that can be attached to a licence, and s 63 provides that nothing in Part 3.5 prevents other conditions being attached to a licence.
64In Botany Bay City Council v Saab Corporation Pty Ltd [2011] NSWCA 308 the Court of Appeal reaffirmed that the scope and purpose of the statutory power being exercised is central to consideration of the limits on the power to impose conditions. The statutory power to impose conditions on transfer of a EPL is framed by reference to the considerations in s 45, which specifies the matters to be taken into account in exercising functions under Part 3, and more generally, by the objects of the Act which are set out in s3, and which relevantly include:
(a) to protect, restore and enhance the quality of the environment in New South Wales, having regard to the need to maintain ecologically sustainable development,
...
(d) to reduce risks to human health and prevent the degradation of the environment by the use of mechanisms that promote the following:
(i) pollution prevention and cleaner production,
...
(iia) the elimination of harmful wastes,
(iii) the reduction in the use of materials and the re-use, recovery or recycling of materials,
(iv) the making of progressive environmental improvements, including the reduction of pollution at source,
(v) the monitoring and reporting of environmental quality on a regular basis,
65As is the case for the issue of an EPL under s53, the transfer of an EPL relates to a specified person. While the EPL must specify the premises to which it applies (s56 POEO Act), an EPL is different to a development consent under the EPA Act which operates in rem, and in relation to which Preston CJ observed in Jonah Pty Ltd v Pittwater Council (2006) 144 LGERA 408 at [35] that in considering whether to grant or modify a development consent, it is irrelevant to enquire as to who is the current owner/operator, or who might be the future owner/operator, or whether the present owner/operator has in the past acted or used the land unlawfully, or whether the future owner/operator is likely in the future to act or carry out any approved use unlawfully.
66Given the nature of an EPL, and the legislative framework which governs the granting and transfer of an EPL, in my view the identity, and where relevant past conduct, of a proposed holder of an EPL are relevant factors in considering whether an EPL should be transferred, and the conditions which should be imposed on such a transfer. The focus of the evidence, and the parties' submissions, in these proceedings has been on the matters specified in s 45(c), (d), (f) and (f1) of the POEO Act. Aspects of the consideration of whether the person to whom the licence is to be transferred is a fit and proper person under s 83 in relation to a proposed transferee that is a body corporate include whether a director of that body corporate is or has been the director of another body corporate that has contravened any of the environment protection legislation or other relevant legislation (s 83(2)(b)(ii)), the record of compliance with environment protection legislation of any director (s 83(2)(d)), whether the management of activities or works will be in the hands of a technically competent person (s 83(2)(e)); and more generally, whether the person has demonstrated the financial capacity to comply with obligations under the proposed licence (s 83(2)(m)).
67While it is correct, as Always submits, that s 225 of the POEO Act provides that payment of a penalty imposed in a penalty notice is not to be regarded as an admission of liability, the evidence of the issuing of Penalty Notices, Clean Up Notices and Official Cautions to No 1 while Mr Matta was its sole director and while it was in control of operations at the site, goes to management of the site and the extent of compliance in the past, and is relevant, together with other evidence including that provided by Mr Matta, in assessing the prospects of future compliance.
68Based on the evidence of Mr Robert Hogan, Manager Waste Operations of the EPA (exhibit 11), the surveys in evidence, and the evidence on the view, I am satisfied that the operation of the site has not been consistent with the General Arrangement Plan approved as part of the SMP: internal access roads and external circulation roads are not clearly defined; waste has been placed across areas marked as being internal access roads; and the walls to contain areas of waste have not been erected as shown on the General Arrangement Plan. The provisions of the SMP have not been complied with, in particular the drive over mounds and proposed pollution control works have not been installed. I accept the evidence of Mr Hogan and Mr Beaman that there is no dirty area kept separate from upstream and clean areas by bunds and roll over mounds; there are no separate and defined areas for the receipt, storage and processing of waste; and the barriers around the areas are not appropriately designed for stormwater management. I accept the evidence of Mr Hogan that in the absence of the components of the SMP there is the potential for stormwater with high suspended solids and gross pollutants to enter the stormwater system.
69Based on the survey evidence, the volume of material and the area and height of the stockpiles of material has increased over time between September 2009 to September 2011. There is an inconsistency between the maximum height specified in the Project Approval for "unprocessed or baled materials" of 3m, and the heights specified in condition L5.2.1 of the EPL, which permit higher stockpiles on specified parts of the site. It is not apparent from the evidence before me how the EPA came to issue an EPL inconsistent with the Project Approval. Regardless of the reasons for that inconsistency, Mr Schlick and Mr Hogan agreed that based on the surveys, as at 6 September 2011 the EPL heights were exceeded in five locations, by 2 m to 8 m; as at 23 February 2012 the EPL heights were exceeded in four locations, by 1 m to 5 m (exhibit 13).
70Mr Matta's evidence was that he intends to comply with the environment protection obligations imposed by the legislation and by the EPL if transferred, and that he is confident that Always can bring the site into compliance including removing the asbestos stockpiles and completing the requirements for stormwater management. There are a number of reasons why I do not share Mr Matta's confidence, based on the present state of the site and the past operation of the site under Mr Matta's control:
(a) The stockpiles exceed the height permitted under the Project Approval, and under the EPL. The evidence of Mr Alex Bourne, Regional Operations Officer - Waste Operations Section (exhibit 5), which was not disputed, was that the height of the stockpiles and the absence of height markers was brought to the attention of Mr Matta as early as April 2010. The surveys of 1 May 2011, 6 September 2011, 23 February 2012 establish that instead of taking action to reduce the stockpiles, they have increased, and now exceed the permitted height to a significant extent. While I accept that No 1 went into liquidation in January 2011, it was not in dispute that Always, and Mr Matta as its sole director, has continued operation of the site since then. Mr Schlick's evidence was that there has been some reduction in the stockpiles since the survey of 23 February 2012; however it was agreed that the stockpiles are still in excess of the permitted height. While I accept that Mr Schlick manages the day to day operations of the site, his evidence that it is Mr Matta who makes the decisions about the stockpile heights was not disputed.
(b) The presence of asbestos in two of the stockpiles has been an issue since May 2010 when the first of the Clean Up Notices was issued by the EPA. The asbestos has not been removed, despite Mr Matta's oral evidence that the removal of the asbestos is not a difficult operation.
(c) The present site layout is not consistent with the approved General Arrangement Plan, and the SMP has not been implemented. Mr Matta's evidence was that the dirty runoff is being contained due to use of hay bales. I accept the evidence of Mr Beaman that hay bales are a temporary solution, and not a permanent measure. Mr Schlick accepted in oral evidence that the SMP has not been implemented and the dirty areas are not in a self contained catchment separate from clean areas, and accepted that there has been no formal assessment of the effectiveness of the hay bales and shipping containers in containing dirty water runoff. Mr Matta's evidence that the approved stormwater management plan has been installed with the exception of the wheelwash and pollution control facility was contradicted by the evidence of Mr Schlick. Based on this evidence, I agree with the EPA that dirty stormwater is both a real risk and an actual problem on the site.
71I agree with the EPA that the site is currently an environmental risk, principally in relation to water pollution from stormwater runoff, and that the presence of asbestos is also a serious environmental risk and human safety concern. I share the EPA's concerns as to Mr Matta's approach to compliance while the site was operated by No 1, in particular his reliance on extended correspondence with the EPA to support his position that the clean up notices had been complied with, while the stockpiles the subject of those notices remain.
72The failure to install infrastructure required by the Project Approval, which was substantially unexplained, and failure to manage the site in accordance with the requirements of the Project Approval and the EPL, together with Mr Matta's evidence that it is the receipt of waste, rather than the recycling of it, that is financially lucrative, when considered in the context of the objects of the POEO Act, in particular s 3(d), support a degree of caution in considering the conditions that should be imposed if the EPL is transferred.
Condition L3.1
73The EPA proposes condition L3.1 in the following form:
The licensee must not cause, permit or allow any waste to be received at the premises until it has complied with the requirements of conditions U1 to U7.
74Conditions U1 to U7 require installation of a dust suppression device in the form of a wheel wash or cattle grid (U1.1); installation of permanent stockpile markers around the perimeter of the waste stockpile areas not more than 20m apart (U2.1, U2.2); reduction of all stockpiles within 90 days to no more than 3m (U3.1), and to a total volume of waste of 27,272 cubic metres (U3.2); removal of all asbestos contaminated waste from two identified stockpiles within 30 days (U4.1); provide a sampling regime to determine the waste classification of stockpiled material in the north east stockpile, report, and remove any waste other than the types of waste authorised to be on site (U5); install a stormwater management system consistent with the key components of the 2009 SMP within 90 days (U6); and install concrete jersey barriers at least 1m high to physically separate roadways and storage areas (U7).
75Always proposes condition L3.1 in the following form:
The licensee must cause and permit the premises to be operated in accordance with the licensee's Waste Reduction Plan.
The Plan sets out the manner in which the holder proposes to carry out waste reduction and removal.
76Always proposes amendment to condition U3 to remove the limitation on total volume of waste, deletion of condition U5, and amendment of condition U6 to require installation within 90 days of a stormwater management system consistent with "any Stormwater Management Plan that is approved by the NSW Department of Planning for the premises." The proposed amendments to these conditions are considered below.
77I am satisfied, based on the evidence before me, that compliance with conditions U1 to U7 as proposed by the EPA would bring the site into compliance with the requirements of the Project Approval and the EPL within 90 days of the date of transfer of the EPL, including removal of the asbestos contaminated waste within 30 days. The issue is whether Always should be permitted to receive waste before that occurs.
78Mr Matta and Mr Schlick were confident that Always could comply with the reduction targets identified in the WRP while being permitted to receive waste. I prefer the evidence of Mr Hogan and Mr Beaman that there is doubt as to whether that is possible. Based on the evidence of Mr Hogan and Mr Beaman (exhibits 9, 11), which was confirmed on the view, I am satisfied that the current state of the site is such that it is not physically possible to receive waste until a large amount of waste from the existing stockpiles is either removed or significantly reduced in size; that it would be extremely difficult to properly install the stormwater management system consistent with the SMP until a large majority of the existing stockpiles are either removed or reduced in size; and that compliance with the requirement to demarcate stockpile cell areas requires the removal of a large amount of waste material. I accept Mr Beaman's evidence that the asbestos stockpiles need to be removed before the areas where that material is currently stockpiled can be used for normal processing activities.
79The condition as proposed by the EPA would permit waste processing to occur, and on the evidence of Mr Matta, Always could generate some income from the sale of processed waste. While I accept that that income would be significantly less than Always could expect if permitted to receive waste, the evidence of Mr Acheson and Mr Russo establishes that Always has funds available to it, having made a net profit before tax of $1,367,804 in the six months to 31 December 2011, and having current assets exceeding current liabilities by more than $1 million in the year to 30 June 2011 and the half year to 31 December 2011.
80I am satisfied that the physical condition of the site, including the delay in implementing the required stormwater management systems, in the context where there would be a financial incentive to continue to receive waste in excess of permitted limits, means that it is not appropriate to permit Always to accept waste until compliance with the conditions of the Project Approval and the EPL is demonstrated. Condition L3.1 should be in the form proposed by the EPA.
Conditions U1 to U7
81Conditions U1, U2, U3.1 and U7 are agreed. Condition U3.2 refers to the volumetric limit established in condition L2, and is considered separately below.
82Condition U4 relates to removal of the asbestos stockpiles, and is agreed with the exception of U4.1(d). Condition U4.1(b) requires notification at least 7 days before commencement of removal of the name and contact details of the landfill where the asbestos waste is to be lawfully disposed of. Condition U4.1(c) requires notification at least 48 hours before removal of the date and time that removal will commence. Condition U4.1(e) requires that Always provide copies of all receipts, dockets and invoices for the removal, transport and disposal of each load of asbestos waste within 40 days from the date of transfer of the licence.
83Condition U4.1(d) as proposed by the EPA requires that removal of the waste not commence until the EPA has confirmed receipt of the notifications required in U4.1(b) and (c), in writing; Always seeks the deletion of this requirement. I accept the evidence of Mr Beaman that it is critical that this waste be removed, and that it be disposed of properly in accordance with the requirements of the Waste Regulation. In the context where it is agreed that the asbestos stockpiles must be removed, and can be removed within 30 days of the transfer of the licence, and where the EPA is to be notified in advance of the place and timing of intended disposaI, I am not persuaded that the addition of a requirement that has the potential to delay compliance is appropriate. Condition U4.1(d) should be deleted.
84Condition U5 provides for classification and removal of the north east stockpile, including provision of a sampling regime to determine the waste classification of this stockpile. Always opposes this condition. Based on the surveys, this stockpile is significantly larger than the other stockpiles in both area and height, and as at 23 February 2012 exceeded the height limit permitted under the Project Approval by 5m. I agree with the EPA that it is important not to defer removal of this stockpile, and that a process of sampling and classification of the waste contained in it will provide clarity and assist in ensuring compliance. Condition U5 should be as proposed by the EPA.
85Condition U6 specifies details of the key elements of the SMP that must be implemented, and provides certainty, rather than leaving open the possibility of further delay if approval of an alternative plan is sought, and the condition should be in the form proposed by the EPA.
86Condition U7.1 requires Always within 90 days from the date of transfer to install concrete jersey barriers at least 1m high to separate roadways and storage areas, "as set out on the [approved Plan of Site Operations - the Applicant has supplied a Plan of Site Operations prepared by Matthew Freeburn, registered surveyors, dated 12 March 2012 and amended 14 March 2012, "Ref: 31936-YARD LAYOUT -12.3.12"]". As noted in submissions by the EPA, this plan (exhibit 12, tab 52) is inconsistent with the General Arrangement Plan, and has not been approved by the Department of Infrastructure and Planning. Condition U7.1 needs to be clarified to identify the site plan to which it refers, and to address any requirement for obtaining the approval of the Department of Infrastructure and Planning.
Condition L2
87Condition L2 as proposed by the EPA provides:
The volume of waste at the premises, including any processed materials, must not exceed 27,242 cubic metres.
88Always opposes this condition, submitting that the amount of waste on the site can be controlled by reference to the height limits of stockpiles and the setbacks, and this is provided in the revised site layout plan.
89The EPA submits that imposing a volumetric limit condition sets a clear limit on the amount of waste on the site minimising the risk of waste being stockpiled in the manner that occurred by No 1. Always has proposed removal of waste by reference to volume in its WRP.
90The calculation of the volumetric limit at 27,242 cubic metres was provided by Mr Hogan (exhibit 10 paragraphs [16]-[23]), which he explained was calculated by taking the total stockpile area of the premises and allowing the stockpiles to be the height limit of 3 m. In oral evidence Mr Matta agreed that Mr Hogan had calculated the volumes in accordance with the steps outlined in his affidavit, and that the quantity was not much in dispute between them. Mr Matta stated that the calculations shown on exhibit 16 which shows the revised site plan are those made by Mr Hogan, together with his calculations in handwriting: he has totalled the volume to be 37,000 cubic metres.
91Mr Beaman's evidence (exhibit 9) was that the EPA commonly conducts surveys of licensed waste facilities to determine the size and volume of unprocessed and processed waste stockpiles; imposing a volumetric limit ensures that compliance can easily be checked by regular six monthly surveys; this method been adopted for another waste processing facility in Sydney; and this is the method required for every scheduled landfill site required to pay the waste levy, pursuant to cl 14 of the Waste Regulation. In oral evidence Mr Beaman stated that he did not think that it would be sufficient to regulate the amount of waste on the site by reference to height limits and the site layout: given the history and ongoing management of the site, and the flexibility of the boundary roads, waste could be moved readily and there is nothing to fix the setbacks.
92I accept the evidence of Mr Hogan (exhibit 11) that large volumes of waste on a site can lead to problems including difficulty in managing stormwater, dust and noise; visual impacts for neighbours; difficulty in keeping processed and unprocessed stockpiles separate; and difficulty for the EPA in fulfilling its regulatory functions. I agree with Mr Beaman that the flexibility of the boundary roads, with the concrete jersey barriers, leaves open the possibility that setbacks may not be maintained. I accept that even if the height limit is complied with, there is a possibility that the volume of waste on the site may increase to the point where the management problems identified by Mr Hogan arise. On the evidence before me the main priority is to bring the site into compliance, and there will be an incentive for Always to achieve that with the imposition of condition L3.1. I am not persuaded that at this stage imposing a volumetric limit calculated on a plan yet to be implemented will assist in ensuring compliance, beyond the specification in condition L6 of height limits and setbacks to be achieved. It may be that once the site layout plan and SMP are implemented and the stockpiles reduced, a volumetric limit would assist in minimising the risk of increasing volumes of waste being stockpiled on the site as was the case with No 1. The EPA has the power under s 58 of the POEO Act to vary a licence, including the conditions.
93The deletion of condition L2 requires the amendment of condition U3.2 to require reduction of the total volume of waste on the site by reference to height limits and setbacks. The redrafting of the conditions should address the relationship between condition U3.2 and condition U7.1.
Condition L6
94The EPA proposes condition L6 in the following form:
L6.1 The height of the stockpile of any waste, including any processed materials (whether of waste or any other materials) on the premises, must not exceed:
(a) 22.24metres AHD for any stockpile that is located within eight metres of the southern boundary; or
(b) 24.21 metres AHD for any stockpile that is located within eight (8) metres of the north east boundary; or
(c) 24.00 AHD for any other stockpile on the Premises.
Note: the height limit for all stockpiles is based on a 3 metre height limit from the natural ground level of the Premises.
L6.2 Any stockpile of waste, including any processed materials, along the southern boundary must be kept five (5) metres away from the fence line at all times.
95Always proposes condition L6 in the following form:
L6.1 The height of the stockpile of any waste, including any processed materials, is required to be consistent with the existing Consent for the premises at all times.
Note: the height limit for all stockpiles in the Consent is based on a 3 metre height limit from the natural ground level of the Premises.
L6.2 Any stockpile of waste, including any processed materials, along the southern boundary must be kept one (1) metre away from the fence line at all times.
96I accept the EPA's submission that because the natural ground level varies across the site, it is preferable to specify measurements that provide accuracy in determining the height of the stockpiles, and which can be readily verified by survey. Condition U2 requires installation of permanent height markers around the perimeter of the site that will assist staff and management in ensuring compliance on a day to day basis with the height limit specified in the Project Approval and the EPL. Condition L6 should be in the form proposed by the EPA.
Condition E2
97Condition E2.1 requires provision of a financial assurance on the form of an unconditional and irrevocable guarantee from an Australian bank, building society or credit union in favour of the EPA, prior to transfer of the licence. The EPA proposes the amount of $315,000; Always agrees to provide a financial assurance, but in the amount of $100,000 in addition to the $100,000 presently held by the EPA.
98The EPA originally proposed the amount of $200,000, however Mr Beaman's evidence (exhibit 9, paragraph [66]) was that this would need to be increased if waste is to be stored in the shipping containers which are being used on the site as noise barriers.
99Always submits that $200,000 is appropriate, and refers to Mr Beaman's evidence (exhibit 9 paragraph [92]) that given the value of operating an approved and licensed waste storage and processing facility, other parties who do not have a poor history of compliance and sufficient financial capacity to address the existing issues at the site would be very likely to come forward to apply for a licence. Always relies on a letter dated 1 December 2011 from Mr Michael Hird of BDO, liquidator of No 1, that the liquidator is prepared to assign the EPL and associated bank guarantee in the amount of $100,000 to Always.
100The EPA submits that the financial assurance is particularly important as Always leases and does not own the site; that s 298(1) of the POEO Act requires that a financial assurance be provided by the licensee, which provides an incentive to ensure that licence obligations are met; that once the licence is transferred No 1 is no longer subject to any licence obligations and so the EPA could not make any claim against the financial assurance provided by it; that Always has previously provided a bank guarantee during earlier negotiations regarding the proposed transfer for an amount of $200,000; and that the financial assurance needs to be provided before the transfer as that is when there is the greatest risk of non compliance.
101Section 298(1) of the POEO provides that the conditions of an EPL can require the holder or former holder of a licence to provide a financial assurance. Section 299 provides that a condition requiring a financial assurance cannot be imposed unless the appropriate regulatory authority is satisfied that the condition is justified having regard to:
(a) the degree of risk of environmental harm associated with the activities under the licence, or
(b) the remediation work that may be required because of activities under the licence, or
(c) the environmental record of the holder or former holder of the licence or proposed holder of the licence, or
(d) any other matters prescribed by the regulations.
102The amount cannot exceed the total cost of carrying out the relevant work or program, which is the amount that, in the authority's opinion, represents a reasonable estimate of the total likely costs and expenses that may be incurred in carrying out the work or program required by or under the POEO Act for which the financial assurance is required: s300 POEO Act.
103Mr Beaman's evidence (exhibit 9) that the EPA requires licensed waste facility operators to lodge bank guarantees to cover the majority of the costs to remediate or clean up abandoned sites; that the cost of remediation of the site by removal of the contaminated waste presently on the site would be in the order of $16,200,000; and that the financial assurance would only provide the EPA with funds to implement site controls to temporarily stabilise any environmental impacts if the site was abandoned, was not disputed. Having regard to the matters specified in s299, I accept that it is appropriate to require a financial assurance. However I am not persuaded that the evidence before me establishes a basis for requiring the amount of $315,000. Mr Beaman's calculations were based on the capacity of the shipping containers being approximately 462 cubic metres, and the total cost of disposing of waste in the containers at $115,500 was based on the assumption that each container is filled, and the evidence did not address the actual amounts stored in the shipping containers. I consider that a financial assurance of $200,000 as initially proposed is appropriate. In considering whether that amount should be provided by Always, I note that while s298 refers to a financial assurance being provided by "a former holder of a licence", the basis on which the EPA would be able to rely on the financial assurance provided by No 1, if assigned by the liquidators of that company, was not established by Always. I agree with the EPA that provision of a financial assurance directly by a licensee provides an additional incentive for compliance. Condition E2.1 should be imposed to require Always to provide a financial assurance for the amount of $200,000.
Other conditions
104The parties agreed that condition A3.1 should be deleted and that condition L3.3 should be amended so that the list of types of waste that can be received at the site once condition L3.1 has been complied with corresponds with the waste permitted under the conditions of the Project Approval.