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[2006] VSC 15
Supreme Court of Victoria
2006-02-07
Hargrave J
Original judgment source is linked above.
CONTRACTS - UNCERTAINTY - whether clause in contract imposing an obligation to clean up environmental contamination at expiration of a lease void for uncertainty - commonsense, non-technical approach to be taken to construction of commercial contracts - construction open which accorded with what reasonable business people in the position of the parties would have understood the clause to mean - clause not uncertain.
Unique Lifestyle Investments Pty Ltd v Robertson [2005] VSC 347 at - applied.
DAMAGES - LOSS OF COMMERCIAL OPPORTUNITY - principles to be applied - plaintiff deprived of sufficiently substantial opportunity to secure a profitable second lease - assessment of value of lost opportunity and prospect of it coming into fruition.
Sellars v Adelaide Petroleum [1994] HCA 4; (1994) 179 CLR 332 applied.
Commonwealth v Amann Aviation Pty Ltd [1991] HCA 54; (1991) 174 CLR 64 applied.
INTRODUCTION
1 In the period 1982 until 2004, the plaintiffs were the owners of land situate in Springvale Road, Springvale ("the land"). At the time the plaintiffs acquired the land, it was leased to the defendant ("Mobil"). At this time, Mobil was conducting a petrol station business on the land.
2 Mobil continued to lease the land from the plaintiffs, and to conduct a petrol station business on the land, until the lease expired in November 2000.
3 The lease contained provisions which required Mobil, at the end of the lease, to clean up any contamination at the land in certain circumstances. It is common ground that, at the end of the lease, there was some contamination at the land.
4 The plaintiffs allege that the extent of that contamination was such as to oblige Mobil, under the terms of the lease, to clean up that contamination so as to permit the land to be used for any "as of right" commercial use ("commercial uses") permitted by a specified zoning under the Springvale Planning Scheme ("the applicable zoning"). Mobil contends that the relevant provision of the lease which requires clean up of contamination in certain circumstances is void for uncertainty. Alternatively, Mobil contends that the extent of the contamination at the land at the end of the lease was not of a level which required it to clean up that contamination.
5 To guard against the possibility that the relevant clean up provision of the lease is void for uncertainty, or that the extent of the contamination is not such as to require clean up under the lease, the plaintiffs have brought an alternative claim in nuisance.
6 The plaintiffs claim that, by reason of the failure of Mobil to clean up the contamination at the land as required by the lease, Mobil is obliged to pay them a licence fee for each day that Mobil failed to clean up, until the land was sold by the plaintiffs in November 2004. The extent of the licence fee claim is $575,735.99, together with interest thereon. Further, the plaintiff claims the difference between the price for which it sold the land in November 2004 and the value of the land at that time if it had been cleaned up by Mobil as required by the lease. The amount claimed in this regard is approximately $650,000.
7 In the event that the plaintiffs are able to establish a cause of action for breach of the lease, Mobil raises defences based upon breaks in the chain of causation, remoteness of damage and failure on the part of the plaintiffs to act reasonably in order to mitigate their damage. In addition, Mobil asserts that the plaintiffs' claims are claims for loss of opportunity, which opportunity should be discounted to a substantial degree having regard to a number of vicissitudes which may have operated to prevent the plaintiffs from fully realising the lost opportunity.
8 The openings and evidence in the proceeding occupied 11 days. Some 22 witnesses were called. Most of them provided detailed witness statements. Others attended pursuant to subpoena. There was an eight volume Court Book and other exhibits outside the Court Book were tendered, including voluminous technical guidelines, policies and standards relevant to contamination of land issues. There was lengthy cross-examination of many of the witnesses. Further, there was substantial objection taken to the admissibility of evidence, especially evidence contained in witness statements which had been served prior to trial. Notwithstanding this, there was little dispute as to the facts.
FACTS
9 For almost 20 years commencing in late 1981, Mobil operated a petrol station at the land. From 1982 until November 2000, it did so as lessee from the plaintiffs.
10 A lease from the plaintiffs to Mobil, which contained options for renewal, was due to expire on 12 November 1995. Under this lease, there was no provision which dealt expressly with Mobil's environmental clean up obligations on the expiry of the lease term. In the course of exercising Mobil's option for a further lease term of five years, Mobil's solicitors proposed some amendments to the existing form of lease, with the intent that these amendments be contained in the new five year lease to operate from 13 November 1995.
11 With respect to Mobil's clean up obligations at the expiry of the lease, Mobil's solicitors proposed a clause to cover this issue expressly. The proposal was, in summary, that Mobil's obligation would be limited to clean up to a level of contamination:
"... so as to permit any as of right ongoing use of the demised premises for service station purposes under the then existing zoning." (Original emphasis; underlining added for further emphasis.)
12 There followed correspondence between the solicitors for the parties. In a letter dated 22 June 1995 the solicitors for the plaintiffs stated that the plaintiffs did not accept the proposed restriction to ongoing use for service station purposes.
13 By letter dated 26 June 1995 Mobil's solicitors responded:
"Mobil has instructed us that it would be prepared at the expiration of the Lease to clean-up the premises so as to permit any as of right use of the premises under the present zoning which we understand is 'office zone' under the Springvale Planning Scheme. This would enable the Lessor to have the clean-up of the premises carried out by reference to other commercial uses permitted under this zoning and not necessarily for ongoing service station use. Would this be acceptable to the Lessors?"
14 The plaintiffs accepted the revised proposal from Mobil's solicitors. As a result, a new lease for a five year period commencing 13 November 1995 was drawn-up and executed by the parties ("the lease").
15 Clause 7 of the lease deals with contamination issues. As I have said, it is an entirely new clause from previous leases between the parties in respect of the land. Clause 7 provides:
"7 (a) During the term of this Lease and any renewal the Lessee will comply with the requirements of the Environment Protection Act 1970 (the Act) in respect of the demised premises including satisfying any notices or orders issued under the Act.
(b) At the expiration or prior determination of the term of this Lease or any subsequent renewal (the handover date) the Lessee shall cause (at its own expense) an Environmental Site Assessment (ESA) to be undertaken to establish the level of contamination (if any) then existing at the demised premises. The Lessee shall thereupon at its expense clean up the demised premises to a level of contamination below the then current maximum allowable concentration set or adopted by the Environment Protection Authority so as to permit any as of right ongoing use of the demised premises under the zoning existing at the commencement date namely Office Zone under the Springvale Planning Scheme.
(c) The Lessee shall indemnify and keep indemnified the Lessor against all actions claims liabilities costs expenses or demands arising from or associated with any contamination disclosed by the ESA arising from the use of the demised premises as a service station.
(d) The Lessee shall be permitted to re-enter the demised premises for a period of 30 days following the Handover Date or such longer period as is reasonably required and at the Lessee's cost carry out the works referred to in subclause (b) hereof and then make good any damage caused by such works to the reasonable satisfaction of the Lessor. Until the Lessee shall have fully complied with its obligations under this Clause 7 the Lessee shall pay a licence fee equivalent to the rent and other payments due immediately before the handover date calculated on a daily basis."
16 The reference in cl. 7(b) of the lease to "as of right use" is a reference to the commercial uses which are permitted under the applicable zoning without the necessity to apply for a permit. These uses include a bank, a post office, a medical centre and an office. Other "as of right" uses under the applicable zoning were not commercial uses.
17 There are other clauses of the lease which are relevant. Each of them was contained in the previous form of lease for the period ending 12 November 1995. Clause 4(b) of the lease provides that the plaintiffs, as lessors, undertake:
"4(b) To permit the Lessee within thirty days after the end or sooner determination of the term hereby granted or any extension thereof to re-enter the demised premises and at the Lessee's costs to remove therefrom all signs pumps for petroleum products and fittings and liquefied petroleum gas equipment from the demised premises and at the Lessee's election either to remove or render useless for the storage of petroleum products or other liquids all underground tanks and fittings in or under the demised premises installed or to be installed or used in connection with the business of the Lessee and any replacements of the same and any parts thereof PROVIDED that if the Lessee does render any of such underground tanks or fittings useless it will do so in such a way that the cost of removal of the said tanks and fittings by the Lessors or any subsequent occupier of the premises is not unreasonable AND in effecting such removal the Lessee shall leave the demised premises and all other fittings and fixtures thereon in a clean, tidy and proper workmanlike manner and shall repair and make good any damage caused by such removal to the demised premises or the remaining fittings and fixtures and in particular and without limiting the generality of the foregoing to safely fill any holes caused by the removal of the tanks and repair any damage to any concrete apron footing or foundation upon the demised premises. In the event that the Lessee shall fail to repair or make good as aforesaid the Lessor shall be entitled to perform such works as he may reasonably consider necessary to so repair and make good and the reasonable costs thereof shall be recoverable from the Lessee on demand." (Emphasis added.)
18 I note that cl. 4(b) does not impose any obligation on Mobil to clean up any contamination which may be found in the soil or groundwater at the land when the underground tanks and fittings are removed. I will hereafter refer to the underground tanks and fittings installed by Mobil at the land as, collectively, "the tanks".
19 Clause 5(f)(i) of the lease provides:
"... The underground tanks for the storage of petroleum products and... fittings... under the demised premises installed... in connection with the business carried on thereon... and any parts thereof shall unless the Lessee pursuant to clause 4(b) hereof shall elect to leave same on the premises (in which case the property in such tanks shall revert to the Lessor) remain the property of the Lessee."
20 It appears that by May 2000, Mobil had determined that it would not renew the lease when it expired on 12 November 2000. Accordingly, Mobil commenced preparing itself to hand back the land to the plaintiffs at the expiration of the lease. Mobil's preparations in this regard were coordinated by Gregory Bond, a Remediation Coordinator employed by Mobil. Mr Bond was the Mobil officer responsible for obtaining the Environmental Site Assessment ("ESA") required to be undertaken by Mobil pursuant to cl. 7(b) of the lease.
21 However, it would appear that Mr Bond paid no regard to the terms of cl. 7(b) of the lease in commissioning the preparation of the ESA. As a result, the design of the ESA ignored the terms of cl. 7(b) of the lease. Clause 7(b) of the lease is directed at a clean up of any contamination in the context of the future use of the land for commercial uses permitted under the applicable zoning. Notwithstanding this, Mr Bond frankly conceded that he sought and obtained the ESA on the express understanding that the land would continue to be used as a service station. Mr Bond said that he reached this understanding "right from the start" in May 2000 as a result of being so instructed by Hayden Burge, who was at that time the Mobil Real Estate Coordinator responsible for all matters relating to the purchase and leasehold of Mobil properties in Victoria.
22 Mr Bond invited Handex Australia Pty Ltd ("Handex") to submit a proposal for the preparation of the ESA. In an early proposal by Handex, 16 soil bores were recommended as part of the scope of work. However, Mr Bond requested Handex to revise its proposal, so as to provide for only 10 soil bores. Mr Bond said that he insisted that the number of soil bores be reduced because of his understanding of the Mobil Environmental Remediation Specifications. These are detailed specifications comprising some 161 pages including annexures. It is apparent that Mr Bond felt himself bound by these specifications in managing the remediation of petrol station sites being vacated by Mobil.
23 Mr Bond did not accept that cost was a main concern of his requirement that Handex reduce the number of soil bores to be drilled for the purposes of the ESA. He insisted that he was principally "following the spec". However, I am satisfied that cost was a significant factor in the decision of Mr Bond to limit the number of soil bores to be drilled by Handex as part of the ESA. I do not accept Mr Bond's attempts to downplay the significance of saving cost in his decision to limit the scope of works to be performed by Handex. Indeed, there is documentary evidence to this effect. In an internal Mobil e-mail dated 8 June 2000, Mr Bond stated in respect of quotations received by Mobil from Handex in respect of two sites, including the land:
"As discussed, I have received quotes from Ross Amato at Handex for 'targeted' ESA's for two (2) Lease hand back sites in Springvale. I believe these estimates are significantly excessive, especially when you compare them to estimates from our other consultants interstate for similar size projects. I think we need to speak with Jason Lagowski about their method of estimating, especially in light of their claims of saving MOA[1] money and adding value." (Original emphasis.)
24 Further, when Mr Bond handed over responsibility for dealing with contamination issues at the land to his successor, he stated in the Job Overlap Form:
25 I am satisfied that, in commissioning the ESA, Mr Bond was careful to ensure that the ESA was limited to that required by the specification and no more. In doing so, he was significantly influenced by the desire to save costs. In this regard, I note that the difference between the Handex proposal which included 16 soil bores, and the Handex proposal which was finally accepted and which contained 10 soil bores, was only $4,000 or thereabouts.
26 It is also relevant to note that the commissioning of the ESA was in circumstances where Mobil had no record of any previous environmental investigation of the land. Prior to seeking a proposal from Handex, Mr Bond sought from the Mobil library copies of "any historical remediation data/reports in archives or in the library" for the land. He was informed that no previous reports existed. I note that this was after Mobil had been conducting a petrol station on the land for approximately 19 years.
27 The scope of the ESA was further limited by the election of Mobil to leave the tanks in the ground, rather than remove them and "make good" any damage to the land occasioned by their removal as required by cl. 4(b) of the lease. As appears hereafter, the continued existence of the tanks in the ground prohibited testing for contamination in the immediate vicinity of the tanks.
28 Mr Bond said that the decision to leave the tanks in the ground was based on the general practice of Mobil in respect of any lease hand back, especially one where it was assumed that the site would continue to be used as a petrol station. As a result of Mr Bond's understanding in this regard, he sought quotations for and subsequently commissioned Tanknology Australia to conduct a "tank and line condition report" in respect of the tanks. The testing was done on 5 and 6 July 2000 and the tanks were all reported as "tight". "Tight" means that the tanks were below specified leak detection criteria. The report from Tanknology concludes with the following statement:
"The enclosed Test Results are valid at the time of testing only and make no warrantee (sic) as to future status."
29 On 17 August 2000, Handex published the first draft of the ESA to Mobil. Thereafter, further drafts were sent to Mobil and were the subject of comment and input by Mr Bond. Each of the drafts disclosed that there was contamination of both soil and groundwater at the land. In general, Mr Bond's comments on the draft reports were directed at ensuring that the ESA did not describe the contamination which was found as significant, and towards reducing the scope (and therefore cost) of the further investigations recommended by Handex in the draft ESA reports.
30 By letter dated 24 October 2000, Mobil informed the plaintiffs that it would not be seeking an extension of the lease at its expiration on 12 November 2000. The letter was received by Mr Harry Flicker, a director of the first plaintiff and the representative of the plaintiffs who had all of the material dealings relevant to this dispute. The letter was signed by Mr Burge.
31 It was common ground that this was the first notice by Mobil to the plaintiffs that Mobil did not intend to renew the lease. Given that Mobil had determined this course by, at latest, May 2000, Mobil demonstrated an extraordinary lack of consideration for the commercial interests of the plaintiffs by giving them such late notice. Although nothing turns on this from a legal viewpoint, it is indicative of the arrogant and high-handed manner in which Mobil has treated the plaintiffs throughout the events material to this dispute.
32 Further in this vein, even though Mobil had commenced its preparations for vacating the land as early as May 2000, the ESA was not available to be provided to the plaintiffs at the expiration of the lease, as required by cl. 7(b). The finalisation of the ESA was delayed due to Mr Bond seeking to make amendments to it so as to alter its conclusions and recommendations. In fact, the ESA was not completed until 15 December 2000, more than one month after the expiry of the lease.
33 In the meantime, on 21 November 2000, Mr Burge wrote to the plaintiffs' real estate agent, George Kiper, by facsimile. Relevantly, the facsimile stated:
"All underground petroleum tanks are the property of the owner of the site. Mobil has conducted an environmental site assessment and we will provide a summary report as soon as our consultants issue their report."
34 In writing this letter abandoning any claim to property in the tanks, Mobil seems to have again proceeded in the absence of any consideration of the terms of the lease. As appears above, the provisions of cl. 4(b) do not give Mobil an option to simply take or leave the tanks. Clause 4(b) provides that Mobil must either remove the tanks, in which case it must make good any damage, or "render" the tanks:
"... useless for the storage of petroleum products or other liquids... PROVIDED that if (Mobil) does render any of such underground tanks or fittings useless it will do so in such a way that the cost of removal of the said tanks and fittings by (the plaintiffs) or any subsequent occupier of the premises is not unreasonable..."
35 It was common ground that there was no evidence that Mobil had taken any steps to render the tanks useless, as required by cl. 4(b). On behalf of Mobil, it was submitted that the plaintiffs did not plead any issue concerning a breach of cl. 4(b) of the lease. Accordingly, Mobil was not on notice that it needed to lead evidence on this issue. However, this submission ignores the overwhelming inference from the facts, and the primary position adopted by Mobil in its dealings with the plaintiffs. As I have said, Mobil sought and obtained the ESA on the basis that the land would be used in the future for service station purposes. With this in mind, Mobil sought and obtained a tank and line condition report to confirm that the tanks and lines were "tight". None of the experts who inspected the land and gave written reports or evidence made any reference to the tanks having been decommissioned in any way. Further Mobil participated in discussions with a proposed tenant of the land, Woolworths. Those discussions, which are referred to hereafter, were on the basis that Woolworths intended to use the tanks in the conduct of a petrol station business on the land by it. I find that the tanks were not rendered useless as required by cl. 4(b) of the lease.
36 The ESA was finally completed on 15 December 2000. Its author and project manager was Ross Amato. He was not called as a witness. The ESA was approved by Jason Lagowski, as acting managing director of Handex. Mr Lagowski did give evidence.
37 The ESA is a lengthy document with many annexures. It describes the results of field testing and analysis of soil and groundwater. Based on these results, the ESA contains an assessment by Handex of the risks associated with "the ongoing use of the site as a service station." The ESA contains no assessment by Handex of the risks associated with the future use of the land for the commercial uses permitted under the applicable zoning. This defect in the ESA is a direct result of the failure of Mobil to appreciate the extent of its clean up obligation under cl. 7(b) of the lease and instruct Handex to prepare the ESA accordingly.
38 The ESA is based upon the results of testing from 10 soil bores and five groundwater monitoring wells. I have noted above that the number of soil bores and wells was limited by the direction of Mr Bond.
39 The soil bores and groundwater monitoring wells installed by Handex were principally targeted around the underground petroleum infrastructure comprised by the tanks. As I have said, this infrastructure includes the associated pipes and fittings for the transfer of petrol from the underground storage tanks to the petrol bowsers. However, due to the continued existence of the tanks underground, none of the soil bores or groundwater monitoring wells installed by Handex is in the immediate vicinity of the tanks. As appears hereafter, this had the effect of preventing Handex from testing the soil and groundwater which was likely to be the subject of the greatest contamination.
40 From the first draft of the ESA, it was apparent that the results of soil testing from soil bore number S2G6 ("soil bore 6") established that soil at a depth of 2.5 metres was contaminated with benzene at a level which exceeds the minimum criterion for further investigation and assessment, on any view of the relevant or applicable environmental standards, guidelines or policies. This is significant, because benzene is a known carcinogen.
41 The ESA stated that the excessive contamination at soil bore 6 was the only soil sample which was detected to be above the contamination criteria adopted by Handex for the purposes of the ESA. Handex stated that:
"All other (soil) samples reported analytes below the adopted criteria."
42 As appears hereafter, this statement by Handex as to the extent of soil contamination had the capacity to be misleading. In order to explain this, it is necessary to note that not all soil samples are sent for analysis. First, the soil which is extracted from a soil bore is subject to field testing at regular depth intervals. This field testing is conducted by a photo-ionisation detector ("PID") which gives a hydrocarbon reading in parts per million ("ppm"). Any PID reading in excess of 100 ppm is considered sufficiently high to justify sending a sample of soil taken from the soil bore at that depth to the laboratory for further analysis. In the case of the excessive contamination disclosed at soil bore 6 at a level of 2.5 metres, the PID reading was 950 ppm.
43 A soil sample from soil bore 5 taken at 5.1 metres yielded a PID reading of 1090 ppm. However, no sample from soil bore 5 at this depth was sent to the laboratory for analysis. As appears hereafter, Mobil was unable to explain this error by Handex in its testing procedures for the purposes of the ESA. As I have said, Mr Amato was not called to give evidence. Nor were the driller or geologist responsible for the field testing by Handex. I infer that their evidence would not have assisted Mobil's case.
44 I find that it is more likely than not that if a sample of the soil from soil bore 5 at a depth of 5.1 metres had been sent to the laboratory for analysis, a further area of excessive soil contamination would have been revealed. This should have been obvious to Handex and been referred to in the ESA.
45 The ESA records that initial sampling of groundwater indicated that the groundwater was contaminated. As a result, Handex recommended that two further groundwater monitoring wells be installed in November 2000. This was done. These additional groundwater monitoring wells were in the vicinity of soil bores 5 and 6. Having regard to the excessive contamination disclosed by analysis of the soil sample from soil bore 6, and the elevated PID reading from soil in soil bore 5, it would have been prudent to take soil samples at the time of installing these additional groundwater monitoring wells. There was no dispute between the experts as to the desirability of this occurring. However, Handex took no soil samples when it installed the additional groundwater monitoring wells in November 2000.
46 Notwithstanding that Handex found at least one example of benzene contamination of both soil and groundwater, Handex nevertheless concluded that there were "minimal risks associated with the ongoing use of the site as a service station". In reaching this conclusion, Handex was influenced by the fact that there was "considerable presence of sealed surfaces across the site (which) would be expected to limit risks posed by soil and groundwater contamination". As I have said, this conclusion was based upon the understanding of Handex, as instructed by Mobil, that the proposed use of the land was "as an ongoing petrol station". The ESA does not consider the suitability of the land for any other commercial use permitted by the applicable zoning, especially one which may involve the construction of commercial premises on the land.
47 Handex concluded the ESA by recommending that a further two groundwater monitoring events take place to ascertain whether the groundwater contamination was migrating away from the land and by noting:
"Whilst the current assessment has indicated limited adverse impact to soils and groundwater, there is a need to confirm hydrogeological conditions at the site prior to any new proposed works taking place."
48 On the day before the ESA was completed and delivered to Mobil, Mr Bond made handwritten notes estimating the cost of removing soil in the vicinity of an area of contaminated soil which was identified from soil bore 6. Although the diameter of the instrument used to obtain this soil sample was less than 50 mm, Mr Bond prepared an estimate for soil removal for an assumed area of 24 square metres (4m x 6m) to a depth of 3.5 metres, a total of 84 cubic metres. This is significant, as it demonstrates that the identification of a sample of highly contaminated soil, so as to require clean up or remediation, will involve removing all of the contaminated soil in that area. In estimating the cost, assumptions must be made. When the work is performed, testing can be done and more precise delineation of the contaminated area will be possible.
49 Mr Bond's estimate for the removal of this single "hotspot" of contaminated soil was $5,840, including a contingency of 10 percent. However, he concluded his estimate by writing "allow $6-7,000". Presumably, this allowance was to cater for the possibility that his 10 percent contingency was insufficient to remove all of the contaminated soil revealed once the overlaying concrete was removed and remediation and associated further testing was undertaken.
50 In the meantime, on 24 November 2000, Woolworths (Victoria) Pty Ltd ("Woolworths") submitted an offer to lease the land for a period of 15 years, with four options of five years each, for the purpose of conducting a "Plus Petrol" service station and convenience store ("the Woolworths' offer").
51 The Woolworths' offer was revised on 27 November 2000 to increase the maximum annual rental increase (which was linked to the consumer price index) from four percent to five percent. The Woolworths' offer was accepted by the plaintiffs, subject to formal documentation, on 27 November 2000.
52 The Woolworths' offer stated that:
"It has been assumed that the existing leasehold improvements, including the existing tank farm, will remain when Woolworths take over the site. Should the leasehold improvements be removed from the site by the owner or the previous operator, Woolworths reserves the right to amend this offer."
53 Further, the Woolworths' offer was subject to formal approval from the Woolworths Property Committee and its Board, and the execution of documentation satisfactory to Woolworths.
54 On 11 December 2000, the Woolworths Property Committee, as delegate of the Woolworths Board approved the Woolworths' offer. On 13 December 2000, Tim Macmillan, an assistant property manager of Woolworths, wrote to the plaintiffs' real estate agent Mr Kiper of TBM.com. and advised Mr Kiper of the approval by the Board of Woolworths. Mr Macmillan continued:
"Accordingly, we now look forward to resolution of documentation in a short a timeframe as possible, and execution of documentation following agreement and settling of final legal issues.
Please liaise with Tom Dugdale, Mallesons Stephen Jaques, and myself with development of documentation." (Emphasis added.)
55 There is no doubt that Woolworths were very keen to lease the land, and to do so at the earliest possible time. In December 2000, Woolworths were in the midst of establishing itself as a major petroleum retailer in Victoria and elsewhere in Australia. At the time, Woolworths was expanding its network of "Plus Petrol" sites at a rate of approximately 10 to 15 outlets each year. Steve Webb, a project manager with Claremont Project Management assisted Woolworths in identifying and developing petrol station sites. He described Woolworths' attitude at the time as "go, go, go, go".
56 Further, the position of the land close to a Woolworths' "Safeway" supermarket suited the strategy of Woolworths to establish petrol outlets close to its supermarkets.
57 Woolworths' solicitor, Mr Dugdale, sent the first draft of an agreement for lease and lease to Mr Kiper on 15 December 2000. Mr Kiper provided these draft documents to the solicitor for the plaintiffs, Ashley West of West & Co. By letter dated 22 December 2000 from Mr West to Mr Dugdale, Mr West noted that Woolworths was already in possession of the ESA and sought to achieve the position whereby no agreement for lease would be necessary and the parties would proceed directly to a lease. On behalf of the plaintiffs, Mr West proposed that Woolworths would "take over the site as is, and as assessed in the ESA". This was unacceptable to Woolworths.
58 The urgency with which Woolworths approached the proposed lease of the land was further evidenced by the conduct of Mr Webb, the Woolworths project manager, seeking urgent advice from an environmental consultant over the 2000/2001 new year period. Mr Webb contacted Stephen Diomides on 30 December 2000 seeking an urgent "appraisal" of the ESA. Mr Diomides obliged. By letter dated 5 January 2001 to Mr Webb, Mr Diomides provided a report of his examination and review of the ESA. For present purposes, it is sufficient to note that Mr Diomides expressed the view in his report ("the Diomides report") that the conclusions stated by Handex in the ESA understated "the very high levels of contamination found." Mr Diomides recommended that the extent of the contamination revealed by the ESA be the subject of further investigation, accurate delineation and remediation by removal from the land.
59 On 19 January 2001, Mr Dugdale forwarded to Mr West a revised version of the agreement for lease and the proposed lease. It is apparent that Woolworths were extremely concerned by the comments in the Diomides' report. Accordingly, the draft agreement for lease contained a clause requiring the plaintiffs to complete "the Landlord's Works" within a 12 month period. In the absence of the Landlord's Works being performed within this period, Woolworths reserved to itself the option to either complete the Landlord's Works at the cost of the plaintiffs or to terminate the agreement for lease.
60 The Landlord's Works are described in the "First Works Schedule" of the draft agreement to lease. Clause 2.3 of that schedule relevantly provides:
"Nature of Landlord's Works
2.3 The Landlord's Works comprise:
(a) testing or procuring the testing of the Premises (by soil tests and such other tests as the Tenant may reasonably require) for the presence of contaminants and contamination and for any breaches of Environmental Laws, and obtaining an environmental site assessment report.
(b) (if the environmental site assessment report obtained by the Landlord under clause 2.3(a) of this Schedule indicates that such works are necessary) removing or procuring the removal of all contamination from the Premises and remedying or procuring the remedying of all breaches of Environmental Laws in respect of the Premises so that the level of contamination at the Premises is in accordance with the Environment Protection Authority Victoria guidelines for the level of contamination at premises of the nature of the Premises and the requirements of all relevant Authorities, and so that there are no breaches of Environmental Laws in respect of the Premises; and
(c) (if any works are required under clause 2.3(b) of this schedule), then after such works are complete:
(i) testing or procuring the testing of the Premises (by soil tests and such other tests as the Tenant may reasonably require) for the presence of Contaminants or contamination, and any breaches of Environmental Laws; and
(ii) obtaining and giving to the Tenant a contamination report stating that the Premises comply with clause 2.3(b) of this schedule. If the Tenant does not elect to obtain a contamination report under clause 2.3(d) of this schedule, the report obtained under this clause 2.3(c)(ii) of this schedule. This report will be the Report to be attached to the Lease for the purposes of clause 17 of the Lease; and
(d) if the Tenant is not satisfied with the contamination report obtained under clause 2.3(c) of this Schedule, the Tenant may elect to obtain, at its own cost, a contamination report in relation to the Premises. If this contamination report reveals the existence of Contaminants or contamination or breaches of Environmental Laws that should have been remediated or rectified by the Landlord under clause 2.3(b) of this Schedule, the Landlord must comply with clause 2.3(b) and (c) of this Schedule as if the report obtained under this clause were the report obtained under this clause 2.3(d).[2] If there are any disputes regarding the report obtained under this clause 2.3(d) or a requirement to carry out additional works under this clause 2.3(d), the dispute must be referred to arbitration in accordance with clause 5 of this deed. If the Tenant obtains a contamination report under this clause 2.3(d) and the contents of this report are not rejected by an arbitrator pursuant to a dispute, this report will be the Report to be attached to the Lease for the purposes of clause 17 of the lease; and
(e) removing or procuring the removal of all improvements and other fixtures, fittings chattels, stock and things from the Premises other than the Improvements, and making good any damage caused by such removal; and
(f) ensuring that the Improvements are left on the Premises and are in good order and condition to the reasonable satisfaction of the Tenant. In particular, ensuring that the leaded petrol, unleaded petrol and LPG fuel tanks, pipes and lines forming part of the Improvements;
(i) are free from leaks, waste oil, kerosene, fuel or other liquid or other than water; and
(ii) contain sufficient levels of water so as to ensure that the tanks do not float out due to hydrostatic pressure from ground water; and
(g) if required by the Tenant, rectify any defects in the fuel tanks, pipes and lines disclosed by the testing of them by the Tenant as part of the Tenant's Works; and
(h) ensuring that the surface of the Premises is in good order and condition, compacted, level and sealed and otherwise to the Tenant's reasonable satisfaction;"
61 From the plaintiffs' viewpoint, the requirement that they perform the Landlord's Works presented them with a difficult decision as to whether to execute the proposed agreement for lease. On the one hand, the proposed tenant Woolworths was insisting upon a new environmental site assessment report being prepared and the removal of contamination from the land to its satisfaction. On the other hand, Mobil was insisting that no clean up was required and was refusing to carry out any remediation works.
62 In substance, the plaintiffs were placed in the position whereby they were being asked to expose themselves to an obligation to pay for the clean up of the land in respect of any contamination identified in a further environmental site assessment to the satisfaction of Woolworths. In respect of this, Mr Flicker recalls a telephone conversation with Mr Diomides in which he was advised that the cost of such a clean up could not be estimated but it could be as much as $1,000,000, or even more. Further, the plaintiffs faced the risk that the cost of clean up might include the cost of reinstalling or replacing the tanks.
63 It was submitted on behalf of Mobil that I should not accept the evidence of Mr Flicker of the telephone conversation which he had with Mr Diomides in which he was advised of the potential cost of clean up. It was submitted that I should reject this evidence because it did not appear in Mr Flicker's witness statement, Mr Diomides gave no evidence about it and the telephone log kept by Mr Diomides, which was extensive, made no reference to such a telephone conversation. In my view, I should accept the evidence of Mr Flicker. I was impressed by Mr Flicker as an honest witness who was not given to reconstruction, exaggeration or evasion. Further, it accords with commonsense that, in the face of consistent refusal by Mobil to conduct any clean up at the land, Mr Flicker would give consideration to the cost to the plaintiffs of conducting a clean up themselves. This is especially so in circumstances where Woolworths had agreed in principle to lease the land on favourable commercial terms, subject to such a clean up taking place. The fact that there is no written record of the conversation with Mr Diomides is relevant but in no sense conclusive. It is likely that the gist of the advice given by Mr Diomides was enough to stifle any further consideration of the option of the plaintiffs arranging for the land to be cleaned up at their cost. In these circumstances, it is not surprising that there is no written record of the conversation.
64 A copy of the Diomides' report (with references to Woolworths masked) was provided to Mobil in February 2001. This did not cause Mobil to alter its position. As a result, a meeting was arranged between the parties and their consultants to discuss the issues and see if the matter could be progressed or resolved. That meeting was held on 20 March 2001 at the offices of Mobil. By the time of the meeting, the concern about identifying Woolworths as the proposed new lessee was resolved. Accordingly, the meeting was attended by representatives of the plaintiffs, Mobil and Woolworths. Mr Diomides attended in his capacity as environmental consultant to both Woolworths and the plaintiffs.
65 The 20 March 2001 meeting was attended by the following persons:
Environmental Consultant for Woolworths and the plaintiffs
Handex Project Manager responsible for preparation of the ESA
66 All persons present at the 20 March meeting, with the exception of Mr Amato and Mr Williams, were called to give evidence.
67 The absence of Mr Williams was not explained. It is curious that he was not called, given that he was the Mobil legal representative present and witnesses recalled him taking notes of the meeting. Those notes are not in evidence. I infer that the evidence of Mr Williams would not have assisted Mobil's case.
68 Attempts were made to explain the absence of Mr Amato. I found these explanations unsatisfactory. It was said it was not known where he was, but there was no evidence of any attempt to locate him.
69 Mr Amato was a relevant witness to much more than the 20 March 2001 meeting. He was the author of the ESA. However, Mobil called Mr Hadwen and Mr Lagowski to justify the ESA, its planning and implementation. I infer that the evidence of Mr Amato would not have assisted Mobil's case on one or more of the issues where evidence from him was relevant.
70 The extent of the recollections of the meeting by those attendees who were called varied greatly. However, it is clear that the meeting lasted for approximately one hour and that the majority of the discussion was of a technical nature, during which the environmental consultants discussed the sufficiency of the ESA, whether further investigation was required to delineate the extent of contamination and whether Mobil had any (and if so what) responsibility to clean up any contamination at the land. Mr Burge summarised these discussions in the following terms:
"The essence of the situation was whether the site was suitable for on-going service station use. We claimed that it was. We acknowledged that there was contamination on the site, but it was no risk to human health, and it didn't preclude its use for service station."
71 Further, the evidence supports the following findings:
(1) The Mobil representatives agreed, at the conclusion of the meeting, to conduct further investigation to delineate the extent of contamination at the land. Specifically, Mobil agreed to install three additional groundwater monitoring wells, two off-site in Springvale Road and one on the land, and two further soil bores in the nature-strip in Springvale Road.
(2) There was some discussion about the possibility of Mobil giving an indemnity to the plaintiffs and/or Woolworths in respect of any contamination at the land. There was reference to a previous arrangement between Mobil and Woolworths in respect of a petrol station site in Patterson Lakes. However, no offer was made to provide such an indemnity and the discussions seem to have been of a conceptual kind only. In final submissions, Mobil did not rely upon any offer to indemnify the plaintiffs and/or Woolworths in respect of any contamination at the land.
(3) There was discussion concerning the state of the tanks. Mr Bond informed those present that the tanks had been tested in August 2000 and found to be tight.
(4) There was discussion about Mobil removing the tanks. Most witnesses could not recall this discussion. However, I am satisfied that there was some discussion on this issue.
72 Mr Burge said that he offered to remove the tanks and that this offer was declined. He could not recall who declined the offer and said "I don't think there was great discussion about it".
73 Mr Bond said that he recalled that there was "talk of removing the tanks". To his recollection, this discussion was between Mr Burge and Mr Flicker. Mr Bond said that Mr Flicker said that he did not want the tanks removed because "he was negotiating with Woolworths, and I think he planned to utilise those tanks".
74 Mr Diomides was asked whether he recalled any party making an offer to any other party at the 20 March meeting. He replied:
"I believe there was a very brief discussion, or an offer by Mobil to remove the tanks, or alternatively to give the tanks to Mr Flicker as the owner of the site, but to my recollection there wasn't any response from Mr Flicker at that time."
75 Mr Diomides was asked if he recalled any offer being made to remove soil as well as the tanks. He responded:
"No. My recollection was there was only reference to tanks, not to any clean up of soil."
76 Although the Mobil witnesses were given every opportunity to give evidence of an offer to remove the packing sand and any contaminated soil around the tanks, none of them could recall that the offer by Mr Burge extended to the removal of any sand or soil. In final submissions, it was submitted on behalf of Mobil that any offer to remove the tanks necessarily carried with it an offer to remove the packing sands and any contaminated soil in the immediate vicinity of the tanks. Reference was made to expert evidence of Mr Mirkov and Mr Hadwen. However, that evidence established only that, before commencing any construction of a commercial building, it would be necessary to remove the tanks and any immediate contamination around the tanks.
77 In my view, the discussion concerning the removal of the tanks did not amount to a formal offer by Mobil. My clear impression from the evidence was that the discussion concerning the removal of the tanks was one of a number of issues discussed in an endeavour to resolve the dispute between the parties as to whether Mobil had any, and if so what, obligation to clean up contamination at the site. In my view, it is more likely than not that the discussion about removing the tanks was in the context of the environmental consultants discussing the need for further testing in order to establish the level of contamination at the land. However, as Mobil placed great weight in evidence and in final submissions on these discussions concerning the removal of the tanks, and for convenience, I will hereafter refer to the statement by Mr Burge that Mobil would remove the tanks as "the Mobil tanks offer".
78 On 16 April 2001, Woolworths applied for and was granted a permit for "Plus Petrol" signage at the land in the event that it became the tenant.
79 By May 2001, the plaintiffs were becoming frustrated by the delays. Accordingly, the plaintiffs proposed that there be a statutory audit of the land under the Environment Protection Act 1970 (Vic) ("the Act"). By this time, Mr Diomides was actively giving advice to the plaintiffs. In order to obtain a statutory audit, he contacted Jonathan Crockett, an environmental auditor appointed under the Act.
80 It is apparent from the correspondence from Mr Crockett at this time that the plaintiffs were most concerned at the cost of a obtaining an environmental audit under the Act. Accordingly, in the first instance, Mr Crockett was engaged to review the ESA to advise whether it would be possible to complete a statutory environmental audit based upon the information contained therein. Mr Crockett advised the plaintiffs that the information contained in the ESA was insufficient to enable him to complete a statutory environmental audit.
81 In a report to West & Co dated 29 June 2001, Mr Crockett was critical of the level of investigation undertaken by Handex as to both soil and groundwater ("the Crockett report"). As to the assessment by Handex that "there appears to be minimal risks associated with the on-going use of the site as a service station", Mr Crockett disagreed and stated as follows:
"5. Risk Assessment
The risk assessment is of a preliminary qualitative nature. It concludes that there is no unacceptable risk but also states that further investigation of groundwater is necessary. More work would need to be done both to confirm that the known contamination, which is well above guidelines, does not present an unacceptable risk and to confirm that the extent of contamination has been adequately delineated.
...
In my opinion, the conclusions in the Handex report are not adequately supported by the investigation carried out and the additional investigation recommended in the report has not been carried out. Thus I suggest that your client may have an adequate basis to request further investigation and if necessary some remediation before accepting that the site has been left in a condition suitable for ongoing use as a service station."
82 As a result of further discussions between Mr Diomides and Mr Crockett, in July 2001 Mr Flicker authorised Mr Diomides to approach the Environment Protection Authority ("the EPA") and seek to have the EPA intervene in the matter by the service on Mobil of a clean up notice under the Act in respect of the land. After initial telephone contact with the EPA, Mr Diomides prepared a letter for Mr Flicker to send to the EPA on behalf of the plaintiffs. In that letter, Mr Flicker referred to the history of the matter, enclosed copies of the ESA, the Diomides' report and the Crockett report and concluded:
"Whereas Handex in their report have chosen to use the term 'limited adverse impact to soils and groundwater,' Diomides & Associates have advised that they believe that this choice of words tends to understate the very high levels of contamination found.
Given Mobil's failure to adequately delineate the extent of contamination caused or to conduct any clean up of the contamination, we urgently request the Authority to intervene in this matter, to examine the attached documents, to resolve whether or not the contamination caused by Mobil in this case contravenes EPA laws and/or regulations, and if appropriate, to serve an EPA Notice on Mobil requiring them to adequately assess and clean up the contamination.
We are negotiating with another operator to take over the site but they will not proceed while the above matters are not resolved, causing us economic hardship whilst this matter awaits resolution."
83 As appears hereafter, it was not until January 2003 that the EPA finally issued a clean up notice to Mobil in respect of groundwater at the land. This delay by the EPA was in the face of repeated approaches by or on behalf of the plaintiffs to have the EPA deal with the matter promptly.
84 In the meantime, another issue arose between the plaintiffs and Woolworths. The issue related to the tanks. By this time, it was apparent that the tanks may need to be removed in order to clean up the contamination at the land. Mr Flicker, on behalf of the plaintiffs, was concerned that this may expose the plaintiffs to the substantial cost of installing new tanks, or at the very least reinstalling the old tanks, in accordance with the draft agreement for lease. Accordingly, on 22 May 2001 the plaintiffs proposed to Woolworths that, if the tanks needed to be removed as part of the clean up of any contamination at the land, then the parties would renegotiate the agreement for lease. This was unacceptable to Woolworths.
85 However, as Woolworths was keen to secure the land, given its expansion plans for its Plus Petrol network and the desirable location of the land in the vicinity of a Safeway supermarket, Woolworths proposed that the draft agreement for lease be amended so as to provide that if the tanks were removed Woolworths would install new tanks at its own cost and, as a result, the annual rent payable under the proposed lease would be reduced by 9 percent of the total costs to Woolworths of installing the new tanks ("the Woolworths tanks offer"). The Woolworths tanks offer was initially put by Woolworths in an e-mail from Mr Dugdale to Mr West on 20 July 2001.
86 There was some delay by the plaintiffs in responding to the tanks offer. Mr Flicker and Mr West were cross-examined to the effect that this delay was because the plaintiffs were considering other opportunities to lease the land. They denied this and I accept their denial. The delay was caused, in part, by the fact that it was the practice of Mr Flicker to travel to Israel around the middle of each year and, in addition, Mr West took holidays in late August or early September. In any event, the issue was an important one from the viewpoint of the plaintiffs and they were entitled to give it detailed consideration. This is especially so when the question of whether the tanks would require removal was uncertain at this time. Woolworths were not insisting that the tanks be removed, only that they required the tanks to be reinstalled or replaced if they were required to be removed as part of the Landlord's Works under the proposed agreement for lease.
87 In the event that the tanks were required to be removed, the agreement for lease does not specify that the landlord must install new tanks. It appears from the proposed agreement for lease and correspondence that Woolworths may have been content for the landlord to reinstate the old tanks or tanks of similar quality without leaks or other defects. However, there is some cause to doubt this. After the meeting of 20 March 2001, Mr Webb telephoned Mr Diomides. Mr Diomides recorded in his phone log that he told Mr Webb that the tanks were 20 to 25 years old and may need to be replaced. Mr Diomides records that Mr Webb responded that Woolworths wanted to lease a complete service station with "viable tanks" and said words to the effect that a test which showed the tanks were "tight" today could show that the tanks were leaking tomorrow.
88 I infer from this that it is likely that, had the tanks been removed as part of a clean up of the land, Woolworths would have insisted that the plaintiffs install new tanks to replace them.
89 By 11 September 2001, it would appear that Woolworths was becoming anxious at the delay in finalising the agreement for lease. In an e-mail from Mr Dugdale to Woolworths, Mr Dugdale summarised the situation at this time:
"The only outstanding issue of any real substance is in relation to the fuel tanks. I confirm that:
1. under the original agreement, the site was to be leased with the existing tanks;
2. as a result of the need for remediation, the tanks may need to be removed. Accordingly, the landlord suggested that if the tanks were removed, Woolworths could have the option to either end the agreement or endeavour to negotiate a suitable amendment to the commercial terms with the landlord;
3. in an endeavour to obtain certainty, we advised the landlord's solicitor that we would accept that if the tanks were removed, the rent would decrease by 9% of the costs of installing replacement tanks. The landlord is still to respond to this suggestion."
90 Mr West finally responded to the tanks offer by e-mail dated 20 September 2001 to Mr Dugdale. Mr West stated in his e-mail:
"Dear Tom,
It would appear that all points of contention have been negotiated save for the matter of the tanks.
The latest update from Steve [Diomides] is that further tests were ordered by the EPA, and that Steve was waiting to speak to the EPA to determine what the current position is and what (if any) formal notices have been served.
Our clients are happy to sign the agreement/lease immediately, save that if the tanks have to be removed due to the Auditor's recommendation in order to comply with any order of the EPA, then the matter should be renegotiated by the parties. Since no-one (whom Steve [Diomides] has asked anyway) can determine an approximate value to replace the tanks, to renegotiate would seem a fairer option of the parties.
Regards
Ashley West
West & Co."
91 Mr West said that he intended his e-mail to be a rejection of the Woolworths tanks offer. Mr Dugdale said that he understood Mr West's e-mail to be a refusal of the Woolworths tanks offer.
92 By e-mail dated 20 September 2001, Mr Dugdale forwarded a copy of the e-mail from Mr West to Woolworths, and stated:
"From the tone of the e-mail, it would appear that we are still the preferred tenant for the site.
I agree with the landlord's solicitor that the situation regarding the tanks is the only outstanding issue. Should I agree to his suggestion (and perhaps include a requirement for both parties to act reasonably and in good faith in the negotiations to tighten up the requirement to negotiate), or should I insist on making our position completely secure by agreeing to the rent reduction now rather than leaving it open for negotiations in the event that the tanks are removed?"
93 No agreement was ever reached between the plaintiffs and Woolworths concerning the tanks. In an e-mail dated 10 January 2002 from Mr Dugdale to Barry Cloke (who had by this time replaced Mr Macmillan), Mr Dugdale noted that he was still to receive instructions from Mr Cloke's superior, Terry Ludlow, in response to his e-mail of 20 September 2001.
94 By a letter of 8 November 2001 from Mr West to Mr Dugdale, Mr West stated the position of the plaintiffs at this time:
"We refer to our e-mail to you of 20 September 2001 and note no reply to date.
Since your client could sign the existing agreement/lease and be able to renegotiate or withdraw if unable to renegotiate, there does not seem to be anything preventing the final amendment and signing of the Agreement."
95 This was the last correspondence from Mr West to Mr Dugdale. It demonstrates that the plaintiffs were prepared to sign the draft agreement for lease, including the obligations to perform the Landlord's Works, subject only to amendment to deal with the situation if the tanks needed to be removed as part of the clean up of contamination at the land.
96 Mr Dugdale said that he received no further instructions from Woolworths in response to his e-mail of 10 January 2002. Mr Cloke said that, in response to Mr Dugdale's e-mail of 10 January 2002, he instructed him to stop negotiating with the plaintiffs because they had rejected the Woolworths tanks offer. Mr Dugdale did not recall this instruction. However, as late as 5 July 2002, Mr Kiper spoke with Mr Cloke and was told that the Woolworths' file for the land was still open and that Woolworths would like to be advised on the progress of the clean up of contamination at the land. Mr Kiper confirmed this conversation in a letter dated 5 July 2002 to Mr Flicker. Although Mr Kiper referred in evidence and in his letter to a conversation with "Mr Gary Cook, Property Manager at Woolworths" I infer that this was a mistaken reference to Barry Cloke. As I have said, Mr Cloke succeeded Mr Macmillan as the property manager at Woolworths responsible for the opportunity to lease the land. It is likely that Mr Kiper had not dealt with Mr Cloke before, and this explains his mistake. In my view, notwithstanding Mr Cloke's evidence, Woolworths did not lose all interest in leasing the land in January 2002. It is more likely that it chose to wait and see what action was taken by the EPA in respect of contamination at the land.
97 The evidence does not establish when Woolworths finally lost patience and determined to look elsewhere for a suitable site for a petrol station adjacent to its Safeway supermarket in Springvale Road, Springvale. However, it appears that when an alternative opportunity presented itself, Woolworths determined to proceed and accept that alternative opportunity. Mr Diomides learned of this when, in January 2003, he contacted Mr Webb to tell him that the EPA had finally issued a clean up notice.
98 In the meantime, the plaintiffs maintained their position that Mobil was obliged to clean up the contamination at the land. Mobil continued to deny any responsibility to do so. The plaintiffs, through Mr Diomides, continued to press the EPA to intervene.
99 In August 2001, Handex reported on the results of a groundwater monitoring event at the land in June 2001 ("the June 2001 groundwater report"). This monitoring event was in accordance with its recommendations in the ESA. The results revealed increased benzene contamination at monitoring well 2 ("MW2") from 800 μg/L in July and November 2000 to between 1500 and 2600 μg/L in June 2001. Despite this increase, Handex reported that "concentrations of groundwater contaminants observed at MW2 have remained approximately constant over the sampling events".
100 However, as with the ESA itself, the June 2001 groundwater report was the subject of significant input from Mr Bond of Mobil. In particular, a previous draft of this report had referred to there being "significant groundwater contamination" at the land. Mr Bond directed that this be removed from the final report. Handex complied.
101 On 22 August 2001, Mr Bond and Mr Lagowski met with representatives of the EPA. The EPA representatives raised a number of concerns about the contamination at the land. One of the EPA representatives at this meeting, and who had the conduct of the matter for some time thereafter, was Michael Rehfisch.
102 On the same day, Mr Rehfisch wrote to Mr Bond and summarised the concerns of the EPA, as expressed during the meeting. Although the focus of the EPA concerns was groundwater contamination, the letter referred to concerns about soil contamination also. In this regard, Mr Rehfisch stated in his letter:
"Further to the meeting, EPA indicated that there are a number of issues that require resolution before considering the need for further assessment and/or monitoring at the site. The issues are as follows:
•
Demonstrate the adequacy and representativeness of the sampling and analysis program for the site. Specifically, EPA notes that the current groundwater flow direction may indicate scope for further investigation of groundwater between the bore SV2MW2 and SV2MW5. Additionally, it appears that field screening for hydrocarbons in soil from S2G5 may not have been confirmed by chemical analysis;
•
Provide details of any tank integrity testing performed at the site, and any other information on potential sources for the hydrocarbon in soil at the site.
EPA believes the above information is important to assist in confirming the nature, extent and magnitude of any risk presented by the site. EPA's requirements regarding ongoing management of the site will be formulated taking this into account."
103 In oral evidence, Mr Lagowski acknowledged that there was discussion at the meeting with EPA representatives concerning soil contamination and, in particular, the failure of Handex to analyse the soil sample taken from soil bore 5 (S2G5) with a PID reading of 1090 ppm. As a result, Mr Lagowski made a note for himself to look at the field notes for soil bore 5 and investigate why the sample was not sent for analysis. However, Mr Lagowski said that he could not recall whether he in fact did so. The only evidence of the instructions given by Mobil to Handex in response to the EPA letter of 22 August 2001 is a facsimile from Mr Bond to Mr Lagowski of Handex. Mr Bond simply forwarded the EPA letter to Handex with the request to "please review their letter and formulate response".
104 Handex drafted the Mobil response to the EPA letter. That response ignored the EPA's expressed concerns regarding soil contamination and, in particular, concerning the failure of Handex to send off the soil sample taken from soil bore 5 for analysis. The response was prepared by Mr Hadwen. He said in cross-examination that the EPA's concerns about soil contamination were overlooked by him, given the focus of the EPA's concerns about groundwater contamination. In this regard, I note that it was accepted by the parties that this focus by the EPA on groundwater was not unusual given the capacity for groundwater contamination to migrate to other sites outside of the subject land.
105 Further, the Handex response was clearly directed towards the continuing use of the land as a petrol station site. It did not consider any other commercial use permitted by the applicable zoning. This is apparent from the terms of the response and was acknowledged by Mr Hadwen in cross-examination.
106 The Handex response concluded with a statement of intention on the part of Mobil to conduct further groundwater monitoring events and, depending on the results, "a site specific risk assessment for on-going service station use may be required". Further, the Handex response referred, for the first time, to the intention of Mobil to prepare a groundwater management plan to review "trigger scenarios" and "possible remedial options for long-term management of the groundwater at the site".
107 Handex concluded its response in the following terms:
"Mobil have indicated an on-going commitment to management of the existing impacts to groundwater at the site. Handex will undertake these works in accordance with Mobil's and EPA's requirements. In the interim, Handex considers that the site is suitable for on-going use as a service station." (Emphasis added.)
108 On 31 October 2001, Mr Williams, as legal adviser to Mobil, responded to a demand from Mr West, on behalf of the plaintiffs, for payment of licence fees. Mr Williams stated:
"Mobil's position is that the conditions under the lease have been complied with and that there is nothing to prevent your client from using the premises as a service station.
This has been the case throughout the period in which your client is claiming that it is entitled to a licence fee.
Accordingly, Mobil denies that it is liable in any way to pay a licence fee to your client." (Emphasis added.)
109 This response confirms the continuing misunderstanding on the part of Mobil, and its legal advisers, that its only obligation under the lease was to clean up contamination so as to permit the premises to be used as a service station.
110 On 28 November 2001, Mr Hadwen of Handex forwarded a draft plan for the management of groundwater contamination at the land to Mr Rehfisch of the EPA. There was no reference in the draft plan to any continued investigation or management in respect of contaminated soil at the land.
111 Handex published a further groundwater monitoring event report in April 2002 ("the April 2002 groundwater report"). This followed the installation of a further groundwater monitoring well in March 2002 which had been installed at the suggestion of the EPA. Once again, this report was the subject of significant input and alteration by Mr Bond of Mobil. In particular, Mr Bond directed, and Handex accepted, the deletion from the final report of references in the draft report to a number of specified potential risks arising from the contaminated groundwater at the land, so that the statement concerning risk was limited to the bland statement:
"Risk:
• Given the current conditions at the site, the risk posed to human health is minimal."
112 At about this time, Mobil was asked by Handex to complete a "customer satisfaction questionnaire". Mr Bond completed the questionnaire. He stated that he was not satisfied with the quality of the "project submittals" by Handex. Mr Bond expanded upon this response in the "additional comments" section of the questionnaire. He wrote:
"Draft report needed significant rewriting to be in accordance with Mobil Spec.
Also, QRA[3] not what was required to submit to EPA."
113 Mr Bond signed this questionnaire on the same day that he forwarded the April 2002 groundwater monitoring report to the EPA.
114 In the meantime, things were moving slowly with the EPA. It may be that, to some extent, the delays were caused by the initial refusal of VicRoads to allow soil bores or groundwater wells to be drilled in the footpath, nature-strip or road adjacent to the land. It appears that the EPA became involved to facilitate this occurring.
115 On 8 May 2002, Mr Rehfisch wrote to Mr Bond:
"Please provide a strategy ASAP for further delineation works at this site - with a view to progressing a proposal for delineation and clean up of polluted groundwater to the extent practicable."
116 In July 2002, Handex published a further groundwater monitoring event report in respect of the groundwater contamination at the land ("the July 2002 groundwater report"). This report contained a qualitative risk assessment, which included the following statement:
"Potential receptors at risk from impacted groundwater include off-site groundwater users and on-site workers, should the impacted groundwater be extracted or should the groundwater be exposed during site works." (Emphasis added.)
117 Further, Handex recommended in the July 2002 groundwater report that a Groundwater Management Plan be formulated "to outline remedial works and ongoing monitoring works".
118 The report concluded:
"Based upon the findings of this GME,[4] Handex considers the site is suitable for ongoing use under its current Business 2 zoning, subject to implementation of a Groundwater Management Plan." (Emphasis added.)
119 Later in July, Handex published a "Groundwater Management Plan". That plan did not deal with any soil contamination issues. The qualitative risk assessment contained within the Groundwater Management Plan concluded:
"It is considered that the only risk from the current status of groundwater contamination at the site exists to onsite workers potentially contacting groundwater during any site redevelopment/ excavation works." (Emphasis added.)
120 The Groundwater Management Plan specified certain "trigger levels" of contamination which would, if revealed by ongoing monitoring, act as a trigger for "contingency action". There were two forms of trigger levels specified. First, if benzene concentrations exceeded 300 μg/L in any monitoring well not then reporting benzene concentrations above that level. Second, for wells already reporting benzene concentrations above 300 μg/L, "a trigger for contingency action will be a sustained increase in benzene concentrations". The focus on benzene was accepted by all of the environmental consultants and auditors who gave evidence as being the form of hydrocarbon contamination with the potential to cause the most serious adverse effect upon human health. This is because benzene is a known human carcinogen.
121 Once a trigger event occurred, the contingency actions specified in the Groundwater Management Plan included notification to the EPA and the formulation of a "Remedial Action Plan... (if necessary)". If a Remedial Action Plan was necessary, then it was to be implemented following discussions with the EPA.
122 Following the completion of the July 2002 groundwater report and the Groundwater Management Plan, Mr Bond left the employ of Mobil. At the time, he completed a "Job Overlap Form" recording the current status of the matters for which he was responsible, including any responsibility of Mobil in relation to the land. In this document, Mr Bond gave a pithy summary of the history of his involvement with the land:
"CURRENT ISSUES OR PROJECTS UNDERWAY: UPCOMING EVENTS:
- ESA complete for lease handback
- no PSH. Dissolved phase plume downgradient of tank farm
- site fit for ongoing use as a S/Stn. Owner & their consultant (Diomides & Assoc) disagree.
- Owner had hoped for Woolworths to take over lease, but deal fell through
- have been unable to delineate plume off-site in Springvale Rd due to services and access refusal from VicRoads
- Owner has gone to EPA to try and get resolution
- EPA gained VicRoads approval for us to delineate with temporary wells only
- EPA require clean-up to extent practicable and on-going management until protection of beneficial uses is restored
- no funds available. Min. spend criteria
- delineation complete. GME and GMP issue to EPA and awaiting approval/comments
- suitable milestone to handover to new consultants if further work required by EPA"
123 This summary by Mr Bond is indicative of his general approach to the issues concerning the land. As far as he was concerned, the ESA had been completed for the purposes of a "lease hand back" so that the land was "fit for ongoing use as a S/Stn". It is apparent that Mr Bond did not understand, or chose to ignore, the terms of cl. 7(b) of the lease which required Mobil to clean up the land so as to permit commercial uses under the applicable zoning. Further, as I have said, Mr Bond's summary establishes that he understood at all relevant times that Mobil wished to spend the minimum amount possible in relation to contamination issues at the land. The attempt by Mr Bond in cross-examination to explain his note "no funds available. Min spend criteria" as being limited to the need for his successor to apply for further funding, in accordance with Mobil internal procedures, was not credible and I reject it.
124 Finally, Mr Bond's summary is relevant because it records that, by August 2002, Mobil were seeking to engage another consultant to replace Handex. This would appear to be the result of Handex ceasing to be on the Mobil panel of preferred environmental consultants to perform environmental site assessments and related work. At about this time, I.T. Environmental (Australia) Pty Ltd ("IT Environmental") appear to have replaced Handex as a panel member to whom Mobil would direct such work. From this time on, IT Environmental advised Mobil concerning its environmental obligations in respect of the land.
125 It was not until 7 November 2002 that Mobil provided the plaintiffs with a copy of the Groundwater Management Plan. This was despite the fact that the plaintiffs had been asking for a copy of it for months. Mobil withheld the Groundwater Management Plan from the plaintiffs and their advisors for the stated reason that it was awaiting legal advice as to whether it should release it. This was typical of the shabby way in which Mobil treated the plaintiffs throughout the dispute. No justifiable reason for seeking legal advice on this issue was put forward. I infer that Mobil was looking for a legal reason to deny the plaintiffs access to the Groundwater Management Plan, because of the perception by Mobil that it may harm it in its dispute with the plaintiffs or that the plaintiff might use the Groundwater Management Plan to make further complaints to the EPA.
126 In particular, I infer that Mobil was concerned to withhold from the plaintiffs, if it could, the results of the qualitative risk assessment in the Groundwater Management Plan and the reference to trigger levels and contingency actions, as set out above.
127 In this regard, it must be recalled that Mobil is a member of a group of companies comprising one of the largest petroleum retailers in the world. It was dealing with two private companies which had invested in real estate for the purposes of obtaining an income. The plaintiffs had no expertise in petroleum contamination or environmental laws. The plaintiffs were in a position where they needed to engage expert advice at considerable cost to themselves in order to deal with contamination issues of which they had no understanding. This must have been obvious to Mobil.
128 Mobil's concerns that the plaintiffs would use the contents of the Groundwater Management Plan to Mobil's disadvantage were well founded. Within a week of receiving the Groundwater Management Plan, Mr Diomides spoke with Mr Rehfisch at the EPA and wrote to him by urgent facsimile dated 15 November 2002. In his facsimile, Mr Diomides was highly critical of the Groundwater Management Plan and, in particular, the lack of any specific remediation action plan in the event that groundwater contamination levels exceeded the trigger levels.
129 In December 2002, Michael Rehfisch handed over the EPA file on the matter to Jennie Slatter. Ms Slatter forwarded a draft clean up notice to Mobil for its comment. Pursuant to s. 62A of the Act, on 16 January 2003, the EPA issued a clean up notice to Mobil in respect of the land ("the clean up notice"). The clean up notice dealt with groundwater only. It made no reference to soil contamination. As I have said, this issue was ignored by Handex in its initial response to the concerns expressed by the EPA in August 2002, and the EPA seems to have failed to follow-up on its initial concerns in this regard.
130 In its covering letter by which it served the clean up notice on Mobil, the EPA stated:
"As previously discussed, this notice formalises the remedial works required at the site.
Please note that the works required by the notice are minimum requirements. If justified complaints are received by EPA, it will be necessary for you to undertake additional work."
131 The clean up notice required Mobil to implement the Groundwater Management Plan which had been submitted by it to the EPA, subject to certain exceptions and additions. One of the additional matters which Mobil was obliged to undertake was to:
"d. Develop a site specific occupational health and safety plan to ensure that there is no undue risk to the health of human beings."
There was no evidence that Mobil developed such a plan.
132 Further, the clean up notice required Mobil to act immediately in the event that groundwater contamination at the land exceeded trigger levels:
"e. Should a trigger level be exceeded in a well not previously reporting concentrations above trigger levels, immediately take measures to implement a remedial strategy at the premises within 3 months of becoming aware of the trigger level being exceeded."
133 Following the service of the clean up notice, Mr West, on behalf of the plaintiffs, wrote a letter of demand to Mr Williams in the Mobil legal department, seeking payment of unpaid licence fees, interest, legal and expert costs and damages for loss of the opportunity to lease the land to Woolworths.
134 There was then some discussion between Mr West and another lawyer in the Mobil legal department, Jolyon Rogers, who had taken over the conduct of the matter from Mr Williams. By facsimile dated 14 February 2003, Ms Rogers responded to the letter of demand sent by Mr West. In her response, Ms Rogers stated on behalf of Mobil, amongst other things, that:
"Mobil maintains its position that it has satisfied its obligations under the lease by handing back to your client a site that was suitable for ongoing use as a service station." (Emphasis added.)
135 Ms Rogers stated that Mobil's position was supported by the ESA, the June 2001 groundwater monitoring report, the July 2002 groundwater monitoring report and the Groundwater Management Plan. Ms Rogers continued:
"I am instructed that these reports, together with the report prepared by Diomides & Associates on behalf of your client, were provided to the EPA prior to the EPA issuing its clean up notice. The subsequent clean up notice is consistent with the Groundwater Management Plan dated 23 July 2002 prepared by Handex on behalf of Mobil. In these circumstances, Mobil considers that your client's claim that Mobil has failed to comply with the lease is untenable.
...
Mobil intends to comply with its statutory obligations under the clean up notice. In this regard, Mobil (or its consultants) will seek the permission of your client to access the site to conduct testing in order to implement the Groundwater Management Plan on each occasion that Mobil's consultants intend to access the site. I am instructed that this testing will involve minimal disruption to your client's use of the premises."
136 There are a number of things to note about the Mobil response. In the first place, the response continues to ignore the requirements of cl. 7(b) of the lease to clean up the land so as to permit ongoing use of the land for commercial uses within the applicable zoning. Secondly, the response ignores the fact that, absent complaint by the plaintiffs to the EPA, it is unlikely that there would ever have been a Groundwater Management Plan. The ESA did not provide for anything other than rudimentary ongoing monitoring of the wells referred to therein. As I have noted, Handex reduced its recommendation as to the number of monitoring wells for ongoing assessment of groundwater, following comments from Mr Bond. Thirdly, the response makes no reference to the fact that the ESA established that one area of soil was contaminated with benzene at levels above investigation levels, whichever levels are adopted. Fourthly, the response is completely silent as to the criticisms of the ESA concerning the failure to analyse the soil samples taken from soil bore 5 which field testing revealed had very high PID readings.
137 In light of the Mobil response, the plaintiffs determined to issue these proceedings. They were issued on 5 August 2003.
138 Whilst the possibility of leasing the land to Woolworths remained alive, the plaintiffs did not actively seek offers to lease or purchase the land. Mr Kiper said that he "did not actively push the property in the marketplace because I knew that the property had a contamination problem and that negotiations were on foot between the owners' solicitor and Mobil to resolve the problem". From the plaintiffs' perspective, it appears that they took the view that Mobil had breached cl. 7(b) of the lease and that, accordingly, Mobil was accruing a liability for licence fees under cl. 7(d) of the lease until the land was cleaned up.
139 In any event, in November 2003 Mr Flicker received an unsolicited expression of interest from the Victorian Government Property Group, on behalf of the Department of Treasury and Finance, for the purpose of identifying a suitable site in Springvale for the development of a new police station. Mr Flicker referred this expression of interest to Mr West. Mr West spoke with the representative of the Victorian Government Property Group and forwarded to him copies of all reports in the possession of the plaintiffs relating to the environmental status of the land. Based on these reports, including a draft of a groundwater monitoring report prepared by IT Environmental in respect of groundwater monitoring events at the land in late 2003, the Department of Treasury and Finance sought its own report from an environmental consultant. That report was prepared by Margaret Mazur of Connolly Environmental (Aust) Pty Ltd ("Connolly Environmental") on 13 August 2004 ("the Mazur report").
140 Ms Mazur was critical of the ESA and, after noting that the plaintiffs did not intend to clean up the site but wished to sell it in its current condition, concluded as follows:
"Summary
Soils and groundwater at the site are impacted by petroleum hydrocarbons, with the uncertain extent of soil contamination. To render the site suitable for the proposed use as police station the service station would need to be decommissioned and the associated contaminated soils removed. Given the identified potential risk to human health due to inhalation of vapors from contaminated groundwater it is also possible that groundwater remediation or implementation of risk management measures would be required to reduce risks to acceptable levels. As the soil contamination is likely to represent a secondary source of groundwater contamination, which appears to remain the responsibility of Mobil, it is unclear who is responsible for clean up of this contamination.
The likely cost of site clean up to enable commercial use (based on remediation by excavation and off-site disposal) is in excess of $210,000 (excluding GST), excluding the cost of groundwater assessment and cleanup or soil cleanup below the groundwater table. If a Statutory Environmental Audit is required, we estimate that a cost of additional $100,000 may be incurred for further site assessment and documentation.
Any future occupier of the site would need to provide access for ongoing monitoring of groundwater and potentially remediation, if warranted.
We strongly recommend that any potential purchaser, in this case the Department of Treasury, be indemnified against future liability, and obtain legally binding assurances regarding responsibility for removal of the remaining sources of groundwater contamination and subsequent groundwater monitoring, management and clean up. In addition we strongly recommend that legally binding assurances be obtained that groundwater monitoring and management or clean up will not interfere with any possible future uses of the site. A meeting with EPA may be advantageous to discuss their views on the proposed development in the light of the existing clean up notice."
141 Based on the Mazur report, the Department of Treasury and Finance did not proceed to consider the land as an appropriate site for the development of a new Springvale police station.
142 In July 2003, IT Environmental had performed works pursuant to the Groundwater Management Plan. Further works were performed in late 2003. A groundwater monitoring report dated 23 January 2004 was prepared ("the January 2004 groundwater report").[5]
143 The January 2004 groundwater report was written by a project supervisor employed by IT Environmental. It was reviewed and approved by Peter Mirkov, an employee of IT Environmental who is an environmental auditor appointed pursuant to the Act. The report states that Mr Mirkov was involved in the writing of the report and that he endorsed "the results as being derived utilising appropriate methodology and with the necessary QA/QC measures". Further, the report states that, although Mr Mirkov "has not written the entire monitoring report he has been intricately involved in the preparation of the report". The relevance of Mr Mirkov's involvement is that he was the expert witness upon which Mobil placed principal reliance. However, his position within IT Environmental demonstrates that he was in no sense an independent expert. Not only was IT Environmental Mobil's paid consultant in relation to the land, as successor to Handex, but IT Environmental was one of Mobil's preferred consultants in respect of similar work.
144 The January 2004 groundwater report refers to the proposed use of the site as "ongoing petroleum facility". I infer that the report was prepared with this in mind, and that it was Mobil who instructed IT Environmental to this effect.
145 In May 2004, the plaintiffs received another expression of interest in the land from Tabcorp. However, this proposal was not pursued as Tabcorp were seeking to have the plaintiffs develop the land for commercial uses, and then lease a portion of the commercial development only.
146 In September 2004, the plaintiffs decided to place the property on the market in its current condition. An auction was arranged for 11 November 2004. The contract of sale and vendor's statement prepared for the purposes of the auction referred to and annexed copies of all of the available environmental assessment reports concerning the land. Accordingly, any prospective purchaser was informed of the results of investigations by Handex and IT Environmental and also of the opinions expressed by Handex, IT Environmental, Diomides & Associates and Ms Mazur.
147 The property was sold at auction on 11 November 2004 for $1,201,000 (exclusive of GST). The purchaser was Mr Avi Silver, a director of United Petroleum Pty Ltd ("United Petroleum"). United Petroleum is a petroleum retailer. United Petroleum intends to develop the land for use as a petrol station.
148 The land has not been used for the conduct of any petroleum business since it was vacated by Mobil in November 2000. In fact, it has not been used at all. It has been fenced off and remained vacant.
149 IT Environmental conducted further groundwater monitoring events in mid and late 2004. Detailed reports were produced.
150 By letter dated 8 September 2005, IT Environmental provided to Mobil a draft of a Groundwater Risk Assessment dated 5 September 2005 and a draft of an undated Interim Groundwater Monitoring Report as a result of a groundwater monitoring event at the land in June 2005. The authors of these documents were not called to give evidence.
151 The covering letter was addressed to Robert Samardjiev, a full-time contractor to Mobil. Mr Samardjiev's title within Mobil is "Project Manager, Global Remediation Australia". In the letter to Mr Samardjiev, IT Environmental stated:
"In accordance with the conclusions reached during our meeting with the EPA (8 March 2005), we have completed the Risk Assessment by considering beneficial uses of the land (commercial uses) as well as beneficial uses of groundwater (Segment C). As agreed with the EPA, the purpose of this risk assessment was to re-examine risks associated with contamination at the site with a view to generating revised trigger levels for the initiation of groundwater remediation action plans. This revision was considered appropriate as the original trigger levels set out in the EPA Clean Up Notice were not deemed appropriate because they did not consider actual beneficial uses.
The risk assessment found that there is unlikely to be any human health risk associated with the ongoing use of the site for commercial purposes (as long as there is no construction directly over tanks and associated infrastructure).
...
In the event that the forecast conditions of the risk assessment are realised, i.e. continuing spread of dissolved phase benzene in groundwater to off-site locations, then it is likely that a remedial action plan will need to be implemented. A RAP will most likely require the removal of what is suspected to be hydrocarbon primary contamination source material within and adjacent to the UST. This will require the removal of the USTs in order to reach the likely secondary source material in surrounding soils." (Emphasis added.)
152 In fact, the groundwater monitoring data annexed to the September 2005 draft Groundwater Risk Assessment revealed, for the first time, that the benzene concentration in one of the monitoring wells ("MW4") exceeded the trigger level adopted in the Groundwater Management Plan. The concentration revealed was 750 μg/L, in comparison to an adopted investigation level of 300 μg/L. Further, the existing exceedance above the adopted investigation levels in MW2 was shown as having increased from 6,800 μg/L in November 2004 to 17,000 μg/L in June 2005.
153 These exceedances of the trigger levels meant that it became necessary for Mobil to implement a remediation action plan in accordance with the clean up notice. According to the 8 September 2005 letter from IT Environmental to Mr Samardjiev, it was likely that the remediation action plan would require the removal of the tanks and "likely secondary source material in surrounding soils".
154 The draft Groundwater Risk Assessment emphasised that it had not been possible to assess the risk to groundwater arising from likely contamination of soil in the area beneath or immediately adjacent to the tanks. This was because no investigations had been conducted of this soil due to the continued presence of the tanks. The draft Groundwater Risk Assessment expressly assumed that any such contaminated soil would not be "left in-situ without being considered for remediation."
155 It is next necessary to note that the plaintiffs served a Notice to Produce on Mobil the day before the trial commenced on 8 November 2005. One of the documents produced by Mobil was an e-mail dated 3 October 2005 from Mr Samardjiev to his supervisor in Mobil, Aaron DeFina. That e-mail ought to have been discovered by Mobil as part of its ongoing discovery obligations.[6] The fact that it was not discovered is regrettable. I infer that, in the absence of the notice to produce, the e-mail would not have been provided to the plaintiffs and would not have been the subject of evidence.
156 The e-mail from Mr Samardjiev to Mr DeFina is set out in full below:
"Aaron,
Meeting notes with United Petroleum (UP):
Attendees:
UP - Avi Silver (Managing Director)
UP - Elias Anastasiou (National Real Estate Manager)
Mobil - Robert Samardjiev
As part of section 3 of the cleanup notice I have further notified UP that a cleanup notice is in force on the site and it is related to Mobil's past use of the site.
I had indicated to UP that the groundwater and soil were Mobil's responsibility for cleanup, as designated by the Victorian EPA. Therefore I have indicated to UP that Mobil would take care of its environmental responsibility and remove secondary source petroleum impacted soil.
UP have indicated that backfilling of the main tank pit is not required as they will be installing new double walled fibreglass tanks themselves. As there are certain Geotechnical requirements with other areas of excavation, UP have requested that all other excavations be left open as well, and that they would take care of the compaction and backfilling in these instances. Yes that's right, we do not have to backfill either!
After reviewing UP's site plans I had offered to level the site (includes building and canopy) on top of taking out the soil, tanks lines and hotspots.
UP have allowed Mobil use of the site until February 2006 (this time to be confirmed - approximate). To be finalised with site contract indicating what Mobil will be doing as part of preparing the site for UP.
As part of due diligence I had offered to keep UP informed and possibly (need to check with you) supply copies of the GME's conducted at the site so they could see that we are remediating the site. Also provide a validation report from the consultant to UP to show that the site has been validated.
I had asked UP that if required, a small remediation system may be installed on site, to this point they had agreed. However we have to work with them to select an appropriate location.
This all sounds to [sic] good, so I would like to get Mobil legal to get a contract in place ASAP so that UP do not turn around last minute and make us pay for re-tanking, backfilling or compaction.
Robert Samardjiev
Project Manager
Global Remediation Australia
Mobil Oil Australia Pty Ltd" (Emphasis added.)
157 As I have said, Mr Samardjiev is a contractor to Mobil. However, he occupies a fairly senior position. Mobil has four or five project managers in Victoria to deal with remediation of contaminated soil and groundwater at petrol station sites occupied, or previously occupied, by it. Some of those project managers also manage remediation projects in other states than Victoria. Mr Samardjiev reports to Mr DeFina, who is the supervisor of Mobil's Global Remediation Group for Victoria, South Australia and Tasmania.
158 After the e-mail was produced and I admitted it into evidence, Mobil filed a witness statement for Mr Samardjiev. Mr Samardjiev gave oral evidence and was cross-examined.
159 Mobil did not raise any issue about the authority of Mr Samardjiev to conduct the meeting with United Petroleum representatives referred to in his e-mail or to make statements or reach agreement with United Petroleum as recorded in the e-mail. Mr Samardjiev said that he regarded the result of the discussions with United Petroleum which are recorded in his e-mail as constituting a verbal agreement. I agree. The subsequent correspondence between Mr Samardjiev and United Petroleum provides ample evidence of this.[7]
160 On its face, the e-mail calls for an explanation. In the first place, it records that Mr Samardjiev stated to United Petroleum representatives that Mobil had a responsibility, as designated by the EPA, to clean up contaminated groundwater and soil at the land. Secondly, the e-mail records that Mr Samardjiev offered to demolish the buildings at the land and to then remove "the soil, tanks, lines and hotspots". In addition, it appears that Mr Samardjiev offered to provide United Petroleum with a "validation report" after these works had been performed, in order to demonstrate to United Petroleum that the land had been "validated". Thirdly, the e-mail states in unequivocal terms that, in the view of Mr Samardjiev, limiting Mobil's clean up obligations to the remediation works offered was of such a benefit to Mobil that:
"This all sounds to (sic) good, so I would like to get Mobil legal to get a contract in place ASAP so that UP do not turn around last minute and make us pay for re-tanking, backfilling or compaction."
161 In his witness statement and in his oral evidence under cross-examination, Mr Samardjiev sought to explain the context in which he made the offer to United Petroleum which is referred to in his e-mail. He also sought to explain or withdraw some of the comments made by him in his e-mail as to the benefit to Mobil of the arrangements with United Petroleum as recorded in the e-mail.
162 Mr Samardjiev was appointed Mobil's project manager in respect of the land in late August 2005. At that time, he received an oral briefing from his predecessor. It appears that the oral briefing was cursory. In Mr Samardjiev's words:
"Pretty much, he just said that there was a case,[8] that there was an issue with the hand over, and that I had to address the clean up notice."
163 Accordingly, Mr Samardjiev came to the task of project managing Mobil's environmental responsibilities with respect to the land without any, or any significant, understanding of the issues between the plaintiffs and Mobil.
164 Mr Samardjiev said that he "briefly looked" at the ESA and the other reports which had been prepared concerning the contamination issues at the land. However, he said that "it is only the more recent groundwater reports that I have actually noticed" and that he viewed his role in relation to the land as in relation to "where the site was at now, and what I needed to do".
165 In this context, Mr Samardjiev said that the focus of his attention was on the most recent groundwater reports, which indicated that the trigger level for benzene contamination had been exceeded at MW4. I have noted this exceedance above. Accordingly, Mobil was required under the terms of the Groundwater Management Plan, as adopted by the clean up notice, to notify the EPA of this exceedance. Mr Samardjiev did so in or about September 2005.
166 In his witness statement, Mr Samardjiev said that, following discussions with representatives of the EPA, he considered a number of options as to what contingency action needed to be undertaken at the land. One option which he considered was the installation of a groundwater remediation system at the land. Such a system would involve pumping out contaminated groundwater and safely disposing of it. A second option which Mr Samardjiev considered was, in his words, "to remove any soil affected". The unstated assumption underlying this second option was that it was contamination in the soil which was causing the groundwater to become polluted. In my view, there is no other rational explanation for the choice of the words "soil affected" appearing in Mr Samardjiev's witness statement.
167 Mr Samardjiev said in his witness statement that he preferred the second option as the "most effective" for Mobil because it would reduce the level of ongoing monitoring at the land and would also reduce the likelihood of Mobil needing to maintain ongoing active or passive attenuation programs. In oral evidence, Mr Samardjiev said that his reference to the second option being the "most effective" was a reference to the fact that it would be "more cost effective" for Mobil to adopt that option.
168 In cross-examination, Mr Samardjiev sought to explain the second option, of removing "any soil affected", as not being necessitated by the need to remove contaminated soil. He said that he had discussed the removal of the tanks and soil with Michael Hill of IT Environmental and Mr Rehfisch of the EPA. Each of them had supported the view:
"... that it would be good to get to the source zone, or the area where there is the most impact in the groundwater. Ideally that would be the case, the most cost effective solution... This was just an ideal case, this was prepared for if we could get down there to remove most of the impact, then it would be better for us."
169 I accept that the one of the reasons for Mr Samardjiev proposing to United Petroleum that Mobil would remove the tanks, and any contaminated soil surrounding them, was to enable a quicker and more cost effective means of dealing with the increased benzene contamination in the groundwater. However, this does not explain a number of the statements and comments in Mr Samardjiev's e-mail. In particular, it does not explain why Mr Samardjiev:
(1) stated to United Petroleum representatives that the soil at the land was "Mobil's responsibility for clean up" and that "Mobil would take care of its environmental responsibility and remove secondary source petroleum impacted soil";
(2) offered to United Petroleum that Mobil would, in addition to removing the tanks and surrounding soil, also take out the "hotspots" (a reference to areas such as the benzene contamination found at soil bore 6);
(3) believed that Mobil was or may be required to "pay for re-tanking, backfilling or compaction";
(4) thought that a result whereby Mobil avoided having to install new tanks, backfill and compact the new soil was something that "all sounds to (sic) good".
170 In cross-examination, Mr Samardjiev sought to explain some of these statements. At first, he accepted that he thought Mobil was responsible for the cost of "re-tanking" (and, I infer, the associated backfilling and soil compaction). However, he then said that this belief was based upon a concern in his mind that Mobil may expose itself to a claim by United Petroleum for "some compensation" in the event that Mobil was unable to complete its proposed works, as offered in the e-mail, by February 2006. This was the date by which United Petroleum indicated to Mr Samardjiev that it wished to complete its own redevelopment and commence petrol retailing operations at the land. Notwithstanding this explanation, Mr Samardjiev could not explain why he did not refer in his e-mail to the possibility of United Petroleum seeking compensation, but instead used "those three particular terms" (a reference to "re-tanking, backfilling or compaction").
171 As to the acknowledgement to United Petroleum that Mobil was responsible for clean up of petroleum impacted soil, Mr Samardjiev said that this statement was based upon discussions which he had with Mr Rehfisch of the EPA "who indicated that ideally, because the groundwater was our responsibility, that we should attempt or just look at the soil as well".
172 As to the tone of the e-mail overall, and in particular the express statement that "This all sounds to (sic) good", Mr Samardjiev sought to retract that view in evidence. He said:
"I wouldn't say it was a good deal, it was, it came out - it was more, lets say it was more cost effective."
173 I reject these attempts by Mr Samardjiev to rationalise the statements and comments made by him in his e-mail. In my view, the statements and comments made by Mr Samardjiev in his e-mail reflected his honest recollections of the meeting with United Petroleum representatives and represented his honest beliefs at the time. Much of what he was offering to do conformed with the observations by IT Environmental in its letter of 8 September 2005 to Mr Samardjiev as to the likely requirements of a remedial action plan if the trigger levels for groundwater contamination were exceeded. That was the very situation which confronted Mr Samardjiev and with which he was principally concerned.
174 To the extent that the plaintiffs rely upon Mr Samardjiev's e-mail as containing admissions that Mobil had the responsibilities referred to in the e-mail, great care needs to be taken in identifying the significance of any admissions. This is because the question of Mobil's responsibility is either a question of law for me to decide or, at best, a mixed question of fact and law. In this regard, I do not accept that Mr Samardjiev's statements and comments can be treated as admissions upon which I could base a finding that Mobil was in breach of its clean up obligations under cl. 7(b) of the lease.[9]
175 However, this does not mean that the statements and beliefs of Mr Samardjiev are of no relevance. As I have said, the statements and beliefs of Mr Samardjiev represent his honest assessment of the situation in circumstances where the trigger levels for contaminated groundwater had been exceeded. Further, his statements and beliefs are consistent with the observations of IT Environmental as to the likely requirements of a remedial action plan in such circumstances. Finally, given Mr Samardjiev's position within Mobil, and his experience and qualifications, I am entitled to, and do, give some weight to his views as to the appropriate action for Mobil to take in order to clean up the contamination at the land.
176 There is another aspect of the evidence of Mr Samardjiev which is of some concern. Notwithstanding Mr Samardjiev's honest belief that Mobil has a responsibility to clean up the contaminated soil and groundwater at the land, which is at least in part based upon the obligations of Mobil under the clean up notice, Mobil had not, as at the time Mr Samardjiev gave evidence, performed any of the works referred to in Mr Samardjiev's e-mail. This is notwithstanding the concerns of Mr Samardjiev that delay in performing these works may expose Mobil to claims by United Petroleum for compensation as a result of any delay in United Petroleum commencing petroleum retailing operations at the land. Further, the clean up notice required Mobil to perform these works within three months of becoming aware of groundwater contamination exceeding trigger levels. At the very latest, this period expired on 8 December 2005, three months after receipt by Mobil of the letter from IT Environmental and enclosed reports. Mr Samardjiev gave evidence on 23 November 2005.
177 This situation has been brought about because Mobil's solicitors discovered what Mr Samardjiev was proposing in relation to the land and put a stop to it. Mr Samardjiev gave evidence that he has been directed by Mobil's solicitors to put all of the proposed works by Mobil at the land "on hold" pending the completion of the hearing in this proceeding. This direction was first given in October this year, shortly before the commencement of the trial.
178 Notwithstanding this direction, Mr Samardjiev saw no harm in proceeding to put in place all of the necessary preparatory steps to enable the proposed clean up works at the land to proceed once the hearing of this proceeding was completed. Accordingly, he applied for relevant demolition permits and the like, and corresponded with United Petroleum representatives concerning schedules of works and timelines. It appears that this conduct by Mr Samardjiev also came to the attention of Mobil's solicitors. As a result, Mr Samardjiev was directed to cease all preparatory work, including applying for permits and discussing schedules and timelines for the proposed clean up works with United Petroleum.
179 Having regard to the dates of various e-mails concerning scheduling and timelines, I infer that this later direction was given to Mr Samardjiev during the course of the trial or very shortly before the trial commenced. When Mr Samardjiev was asked whether he was having continuing discussions with representatives of United Petroleum concerning Mobil's proposed clean up works at the land, after his last e-mail to United Petroleum on 4 November 2005, he replied:
"Elias has contacted me on two occasions just to find out where the site is at, and what is happening, and I indicated because of the case I can't talk to you about it, I can't do anything until I resolve it, I don't want to get into any trouble because I'm not sure how the system works."
180 This conduct on the part of Mobil and its solicitors reflects poorly upon Mobil. Not only has it had the effect of delaying Mobil complying with its obligations under the clean up notice issued by the EPA, to the extent that Mobil will in all likelihood have breached the three month period specified in the clean up notice to take remedial action, but it has potentially deprived the Court of evidence as to the actual state of contamination in the soil at the land, particularly the soil adjacent to the tanks. Further, the act of removing the tanks would be likely to reveal the source of the contamination which has been established and of any further contamination which is revealed at that time.
181 I accept that Mr Samardjiev could not say that, if the proposed clean up works had commenced soon after his e-mail on 3 October 2005, the works would have been completed before the end of the trial. Mr Samardjiev said that it was possible that the clean up works may not have been completed by the time he gave evidence, because this would depend upon a number of factors, including the necessary permits being obtained in a timely fashion. However, the fact remains that, by reason of the intervention of Mobil's solicitors, relevant evidence which might have been obtained was not.[10]
UNCERTAINTY AND CONSTRUCTION OF CLAUSE 7
182 It is settled law that it is the duty of a court in construing a commercial contract to approach its task in a commonsense way in an endeavour to give effect to the bargain reached between the parties. It is only where the Court encounters a level of ambiguity which is so obscure as to indicate that the parties did not in fact reach agreement that a court should hold an agreed contractual provision to be void for uncertainty. The relevant principles were recently reviewed by Dodds-Streeton J in Unique Lifestyle Investments Pty Ltd v Robertson[11], where her Honour stated:
"88. Relevant authority establishes that the modern approach to the construction of commercial agreements of business people is, generally, to endeavour to uphold the bargain by eschewing a narrow or pedantic approach in favour of a commercially sensible construction, unless irremediable obscurity or a like fundamental flaw indicates that there is, in fact, no agreement. It is permissible to have regard to extrinsic evidence of the 'factual matrix'[12] or surrounding circumstances in determining the meaning of contractual terms.
89. In Hillas & Co Ltd v Arcos Ltd,[13] Lord Tomlin stated:
'the problem for a court of construction must always be so to balance matters that, without violation of essential principle, the dealings of men may as far as possible be treated as effective, and that the law may not incur the reproach of being the destroyer of bargains.'[14]
90. Lord Wright stated:
'Businessmen often record the most important agreements in crude and summary fashion. Modes of expression sufficient and clear to them in the course of their business may appear to those unfamiliar with the business far from complete or precise. It is, accordingly, the duty of the court to construe such documents fairly and broadly, without being too astute or subtle in finding defects.'[15]
91. In Biotechnology Australia Ltd v Pace,[16] Kirby J, in acknowledging the difficulty of reconciling the competing principles, stated as a general observation that:
'The determination of every case depends upon its own facts. The meaning of the agreement between the parties must be discovered objectively. Where there is suggested ambiguity or vagueness or where it is urged that a term is illusory, it may sometimes be both necessary and appropriate to have regard to extrinsic evidence in order to give meaning to that to which the parties have agreed.
The court will endeavour to uphold the validity of the agreement between the parties. The court will attempt to avoid frustrating the wishes of the contracting parties so far as those wishes may be ascertained from the agreement between them: see Meehan (at 589); see also Barwick CJ in Upper Hunter County District Council v Australian Chilling and Freezing Co Ltd [1968] HCA 8; (1968) 118 CLR 429 at 437 where his Honour said that: "... In the search for that intention no narrow or pedantic approach is warranted, particularly in the case of commercial arrangements."
But the court will not do so, where, in effect, it is asked to spell out, to an unacceptable extent, that to which the parties have themselves failed to agree. Nor will the court clarify that which is irremediably obscure ... '. [17]
92. In Vroon BV v Fosters Brewing Group Ltd,[18] Ormiston J also stated 'that in commercial transactions the court should strive to give effect to the expressed arrangements and expectations of those engaged in business, notwithstanding that there are areas of uncertainty and notwithstanding that particular terms have been omitted and not fully worked out' whilst acknowledging that '[w]here one should draw the line is difficult to state and equally difficult to apply'.[19]
93. Consistently with the above principles, in MLW Technology Pty Ltd v May,[20] Gillard AJA, (with whom Winneke P and Buchanan JA agreed), stated:
'The court, in construing contracts between businessmen and also their actions, should proceed in a commonsense, non-technical way. How would the businessmen construe the agreement in the light of the commercial purpose of the setting ... '[21]
'Since then there has been a shift from strict construction of commercial instruments to what is sometimes called purposive construction of such documents ... It is better to speak of a shift towards commercial interpretation. About the change in approach to construction there is no doubt. ... In determining the meaning of the language of commercial contract, and unilateral contractual notices, the law therefore generally favours a commercially sensible construction. The reason for this approach is that a commercial contract is more likely to give effect to the intention of the parties. Words are therefore interpreted in the way in which a reasonable commercial person would construe them. And the standard of the reasonable commercial person is generally hostile to technical interpretations and undue emphasis on niceties of language.'"[24]
183 The most recent statements of principle by the High Court as to the task of a court in construing a commercial contract, and as to the material available, are consistent with the above quoted passage. The task of a court in construing a clause in a commercial contract is to be determined by a consideration of what a reasonable person in the position of the parties would have understood the clause to mean. In Pacific Carriers Ltd v BNP Paribas[25], Gleeson CJ, Gummow, Hayne, Callinan and Heydon JJ stated:
"The case provides a good example of the reason why the meaning of commercial documents is determined objectively: it was only the documents that spoke to Pacific. The construction of the letters of indemnity is to be determined by what a reasonable person in the position of Pacific would have understood them to mean. That requires consideration, not only of the text of the documents, but also the surrounding circumstances known to Pacific and BNP, and the purpose and object of the transaction. In Codelfa Constructions Pty Ltd v State Rail Authority of NSW, Mason J set out with evident approval the statement by Lord Wilberforce in Reardon Smith Line Ltd v Hansen-Tangen:
'In a commercial contract it is certainly right that the court should know the commercial purpose of the contract and this in turn presupposes knowledge of the genesis of the transaction, the background, the context, the market in which the parties are operating.'" (Citations omitted.)
184 In Toll (FGCT) v Alphapharm[26], Gleeson CJ, Gummow, Hayne, Callinan and Heydon JJ stated:
"This court, in Pacific Carriers Ltd v BNP Paribas, has recently reaffirmed the principle of objectivity by which the rights and liabilities of the parties to a contract are determined. It is not the subjective beliefs or understandings of the parties about their rights and liabilities that govern their contractual relations. What matters is what each party by words and conduct would have led a reasonable person in the position of the other part to believe. References to the common intention of the parties to a contract are to be understood as referring to what a reasonable person would understand by the language in which the parties have expressed their agreement. The meaning of the terms of a contractual document is to be determined by what a reasonable person would have understood them to mean. That, normally, requires consideration not only of the text, but also of the surrounding circumstances known to the parties, and the purpose and object of the transaction."
185 There was no dispute as to the applicable legal principles. It was submitted on behalf of Mobil that the terms of cl. 7(b) of the lease were "irremediably obscure" such as to be incapable of any definite or precise meaning. Accordingly, it was submitted that I should find that cl. 7(b) of the lease is void for uncertainty.
186 Before considering the contention on the part of Mobil that cl. 7(b) is void for uncertainty, it is necessary to note the evidence and agreement of the parties that there is, and has never been, such a thing as a "maximum allowable concentration" which has been set or adopted by the EPA in respect of any form of contamination. The evidence and agreement of the parties establishes that, in considering whether land in Victoria is suitable for any particular use, the EPA, environmental auditors appointed by the EPA and professional environmental consultants have regard to a number of laws, regulations, directions, standards, guidelines and policies. In general terms, these documents are established around investigation levels of contamination. Those investigation levels act as a trigger or threshold for further investigation of the extent of contamination at the land in question, and an assessment of the risk to human health and the environment, in order to determine whether the land in question is suitable for use of any kind, or for a particular use.
187 The argument put on behalf of Mobil as to uncertainty was straightforward. Based upon the agreed fact that the EPA does not set or adopt any "maximum allowable concentration" for contamination of either soil or groundwater present at land in Victoria, it was submitted that the parties failed to reach agreement upon an objective standard to which Mobil was required to clean up the land under cl. 7(b) of the lease.
188 On behalf of the plaintiffs, it was contended that, when regard was had to the terms of cl. 7 of the lease as a whole, and its evident commercial aim or object, the Court should construe cl. 7(b) as imposing an obligation upon Mobil to clean up the land:
" to a level of contamination below the then current maximum allowable concentration consistent with laws, regulations, directions, standards, guidelines or policy then set or adopted by the Environment Protection Authority so as to permit any as of right ongoing use..." (Underlined words inserted in substitution for deleted words; original emphasis.)
189 It was submitted on behalf of Mobil that, even if cl. 7(b) was construed in the way contended for on behalf of the plaintiffs, there is still no readily accessible external standard or criteria against which any clean up of the land is to be measured. In this regard, reliance was placed on the following statement of Kirby P (as he then was) in Trawl Industries of Australia Pty Ltd v Effem Foods Pty Ltd:[27]
"Avoiding the legal frustration of commercial bargains:
There is a natural tendency, entirely understandable, on the part of a judge sitting in the Commercial Division (or elsewhere) to seek to uphold a detailed written document, such as the Heads of Agreement executed by the parties here. I applaud that inclination. I fully understand and support it... No external decision-maker is provided to resolve differences which might arise at or after the promised conferences: cf Godecke v Kirwan. Nor is there a readily accessible external standard to which a court might look to add flesh to the provisions which are otherwise unacceptably vague or uncertain or apparently illusory: cf Meehan v Jones. Nor is this contract one of the kind with which courts have a lawyerly familiarity: so that they may feel confident enough in their abilty to fill in the gaps which the parties have left: cf Charalambous v Ktori.
Instead, what is being sought, the parties having failed to specify their own agreement, is that the Court should complete the pages which the parties left blank. What the Court is asked is to do so in a major commercial undertaking. It is asked to do so although all that the parties actually promised to do was to confer. It is asked to do so although no clue is provided as to exactly what the parties contemplated at the time of their suggested 'agreement'. It is asked to do it by latching onto a pious preambular statement that a price would be fixed which would 'provide a reasonable commercial profit'." (Citations omitted.)
190 I do not accept these submissions on behalf of Mobil. In my opinion, when cl. 7(b) of the lease is construed in the context of cl. 7 as a whole, and in light of its obvious commercial purpose as disclosed by the whole of that clause and the factual matrix against which it was agreed, cl. 7(b) is not so obscure as to indicate that the parties failed to reach agreement as to the standard against which Mobil is obliged to clean up any contamination at the land.
191 The objective factual framework against which cl. 7(b) was agreed has been set out earlier in these reasons. The genesis of cl. 7(b) lay in the concern by Mobil that the previous lease did not contain a provision dealing expressly with Mobil's environmental clean up obligations on the expiry of the lease term. This caused Mobil to propose an initial draft of cl. 7 to be included in the lease. The correspondence between the solicitors for the parties following Mobil's proposal demonstrates, as do the words of cl. 7(b) itself, that the objective aim or object of the parties was to introduce a clause in the lease which specified the extent of Mobil's clean up obligations at the expiry of the lease.
192 In considering whether the words of cl. 7(b) record an enforceable agreement between the parties as to the extent of Mobil's clean up obligation, it is necessary to consider the terms of cl. 7 as a whole.
193 Clause 7(a) imposes an obligation upon Mobil, during the term of the lease, to comply with the requirements of the Act in respect of the land. This obligation is not limited to satisfying any notices or orders issued by the EPA under the Act. Under ss. 39(1)(b) and 45(1)(b) of the Act, it is an offence to "pollute" soil or groundwater at land so as to make, or be reasonably expected to make, the soil or groundwater "harmful or potentially harmful to the health... of human beings".
194 Clause 7(b) has two limbs. The first limb requires Mobil, at its cost, to establish the extent of contamination (if any) existing at the land when the lease expires. This is to be done by means of an ESA ("the ESA obligation"). Establishing the extent of contamination at the land on the expiry of the lease is an important component of the scheme agreed by the parties in cl. 7. In the first place, it is the level of contamination established by the ESA which is to determine whether Mobil has a clean up obligation. Putting to one side the question of agreement by the parties as to the standard of clean up required, such a standard must be applied against the findings of the ESA as to the level of contamination then existing at the land. Secondly, the indemnity granted by Mobil to the plaintiffs under cl. 7(c) is expressly linked to "any contamination disclosed by the ESA".[28]
195 The second limb of cl. 7(b) is obviously intended to record the agreement of the parties as to the standard to which Mobil is required to clean up any contamination at the land ("the clean up obligation"). Although the words used by the parties to describe this standard refer, when construed strictly and pedantically, to a non-existent standard, that does not mean that the words are so obscure that the Court must find that the parties failed to agree upon the applicable standard.
196 In my opinion, the words used in cl. 7 give a clear guide or "clue"[29] as to the standard which the parties intended Mobil was required to clean up. In the first place, as I have noted, cl. 7(a) requires Mobil to, amongst other things, ensure that it does not "pollute" the land (soil or groundwater) in contravention of ss. 39 or 45 of the Act. Further, under cl. 7(a) Mobil is required to comply with any notices or orders issued under the Act by the EPA. Secondly, against a level of contamination established by the ESA, Mobil has agreed to clean up the land to levels of contamination which, by reference to a standard set or adopted by the EPA, will permit any of the commercial uses under the applicable zoning. Although the parties have mis-described the standard set or adopted by the EPA with respect to contamination levels of land, there is no doubt that they intended to impose on Mobil an obligation to clean up the land in accordance with standards set or adopted by the EPA for the purpose of determining whether land will be suitable for commercial uses under the applicable zoning.
197 Next, in considering cl. 7 as a whole, cl. 7(c) imposes an obligation upon Mobil to indemnify the plaintiffs in respect of claims against them "arising from or associated with any contamination disclosed by the ESA arising from the use of the [land] as a service station". This clause provides a clear indication that the parties intended that Mobil would bear the financial cost arising from any petroleum contamination at the land. Although cl. 7(c) is not directly relevant to the issues in this proceeding, it demonstrates the intention of the parties as to the allocation of costs arising from contamination at the land.
198 Finally, cl. 7(d) of the lease contains the agreement of the parties as to the consequences for Mobil if it does not clean up in accordance with the clean up obligation, and as to its responsibilities if it does clean up. If Mobil does not clean up, then it is obliged to pay the licence fee. If it does clean up, it must "then make good any damage caused by such works to the reasonable satisfaction of [the plaintiffs]" ("the make good obligation"). Once again, the intention of the parties is clear. It is Mobil who is to bear the financial consequence of any contamination existing at the land at the expiry of the lease. This includes paying notional rent for the land (the licence fee) until it complies with the clean up obligation.
199 Having regard to the terms of cl. 7 as a whole and the obvious commercial purpose disclosed by it, I reject the submissions on behalf of Mobil that cl. 7(b) of the lease is void for uncertainty.[30] I accept the commercially sensible construction of cl. 7(b) which has been put forward on behalf of the plaintiffs. In my view, that interpretation accords with that which reasonable businesspeople in the position of the parties would have understood cl. 7(b) to mean.
200 No difficulty arises in identifying the relevant laws, regulations, directions, standards, guidelines or policies set or adopted by the EPA in November 2000. In the first place, the Act governed the situation. Second, the principal expert witness called on behalf of the plaintiffs (Anthony Lane) and the principal expert witness called on behalf of Mobil (Peter Mirkov) agreed that, in November 2000, the EPA had regard to the following standards in considering whether land was suitable for any particular use:
(1) Australian and New Zealand Guidelines for the Assessment and Management of Contaminated Sites, issued by the Australian New Zealand Environment Conservation Council and National Health & Medical Research Council (ANZECC/NHMRC 1992 ("ANZECC 1992").
(2) National Environment Protection (Assessment of Site Contamination) Measure issued in 1999 ("NEPM 1999").
(3) Victorian EPA State Environment Protection Policy (Groundwaters of Victoria) 1997 ("Victorian Groundwaters 1997").
201 Mr Mirkov said that other guidelines were relevant to the assessment of whether contaminated land in Victoria was suitable for particular purposes. In particular, reliance was placed by him upon the Guidelines for the Management of Petroleum Hydrocarbon Impacted Land, April 1999 ("Australian Oil Industry Guidelines" or "AOIG").[31]
202 However, the only representative of the EPA who gave evidence, Stuart McConnell, said that the Australian Oil Industry Guidelines have no status before the EPA and have not been reviewed or endorsed by the EPA in any way. I accept this evidence.
203 As appears hereafter, the environmental expert witnesses who were called to give evidence had no difficulty in expressing opinions on the issues raised by cl. 7(b). Opinions were expressed as to the adequacy of the ESA, and whether it established the level of contamination of the land. Further, opinions were expressed as to whether, having regard to the extent of contamination identified in the ESA and which may be inferred to exist in the vicinity of the tanks, the land was suitable for commercial uses under the applicable zoning. The fact that none of the experts had any difficulty in expressing these opinions, supports the commercially sensible interpretation of cl. 7(b) put forward on behalf of the plaintiffs. The experts expressed their opinions by reference to the laws, regulations, directions, standards, guidelines and policies adopted by the EPA in November 2000 in considering whether land was suitable for any use, or any particular use.
204 I turn to consider whether Mobil has breached cl. 7 of the lease.
HAS MOBIL BREACHED CLAUSE 7?
205 Before considering whether Mobil is in breach of cl. 7, it is necessary to consider the relationship between the obligations of Mobil under cl. 7 and the right of Mobil under cl. 4(b) to elect to either remove the tanks or render them useless and leave them at the land
206 The conduct of Mobil from the time it determined that it would not renew the lease has, in my view, been affected by an underlying assumption. Mobil has assumed, and has asked its consultants and experts to assume, that its obligations under cl. 7(b) must be assessed and considered on the basis that the tanks and the immediately surrounding tank sands, soil and groundwater were the responsibility of the plaintiffs ("the tanks assumption"). In my view, Mobil, its consultants and experts were wrong to proceed on the tanks assumption. The option which Mobil had under cl. 4(b) to render the tanks useless and leave them at the land, and thus to assign ownership of the tanks to the plaintiffs under cl. 5(f)(i) of the lease, does not affect the obligations of Mobil under cl. 7(b). It must be remembered that Mobil was not obliged to render the tanks useless and leave them at the land. It had an option to remove them, in which case it was required to "make good". If the only way in which Mobil could comply with its obligations under cl. 7(b) was to remove the tanks, it was in my opinion obliged to do so. It was not open to Mobil to limit the extent of its obligations under cl. 7(b) by electing to leave the tanks at the land and assigning ownership of the tanks to the plaintiffs.
207 By electing to leave the tanks at the land, and assigning ownership of the tanks to the plaintiffs, Mobil exposed itself to the risk that it might be required to remove the tanks in order to comply with cl. 7(b) and, if it did so, to re-install the tanks or replace them with tanks of similar quality in order to comply with the make good obligation.
208 There is another underlying assumption which has affected Mobil's conduct in relation to its obligations under cl. 7(b) of the lease. Mobil has assumed, and has asked its consultants and experts to assume, that its obligations under cl. 7(b) must be assessed and considered on the basis that the continuing use of the land would be for service station purposes ("the service station assumption"). In my view, Mobil, its consultants and experts were wrong to proceed on the service station assumption. The service station assumption is contrary to the obligations of Mobil under cl. 7(b) of the lease. The ESA obligation requires Mobil to establish the level of contamination at the land, and assess any risks arising from such contamination, on the assumption that the land may be used for any of the commercial uses permitted under the applicable zoning. Under the clean up obligation, Mobil is required to clean up so as to permit any of those commercial uses. The service station assumption is inconsistent with both of these obligations.
(1) Clause 7(a): Did Mobil comply with the Act during the term of the lease?
209 Although the plaintiffs alleged in the statement of claim that Mobil breached cl. 7(a) of the lease, and directed brief final submissions towards this issue, it is unnecessary for me to consider this issue in any detail. No submissions were directed towards the assessment of any damage suffered by the plaintiffs by reason only of a breach of cl. 7(a).
210 In my view, it is sufficient to dispose of the cl. 7(a) issue by referring to the fact that the ESA established one area of significant benzene contamination in both soil and groundwater and, in addition, noting that the experts agreed that it was probable that there was further contamination of the land in the vicinity of the tanks. I find that it is probable that this contamination was the result of the conduct by Mobil of a petrol station business at the land during the period of the lease. If this be so, then Mobil has breached cl. 7(a) of the lease by failing to comply with ss. 39(1)(b) and 45(1)(b) of the Act. Those sections prohibit changing the condition of land or water (including groundwater) to the extent that the land or water is, or may reasonably be expected to be, harmful or potentially harmful to the health or welfare of human beings. The contamination which appears at the land includes benzene contamination, which is potentially harmful to the health or welfare of human beings.
(2) Clause 7(b): Did the ESA establish the level of contamination at the land?
211 The principal environmental expert who gave evidence on behalf of the plaintiffs was Anthony Lane of Lane Consulting. The principal environmental expert who gave evidence for Mobil was Peter Mirkov of IT Environmental. I will refer to them jointly as "the experts". Prior to giving oral evidence, each of them prepared an expert witness statement pursuant to Order 44.[32]
212 As the issues developed in the trial, I ordered that the experts confer and provide a joint report to the Court under the provisions of Rule 44.06. I directed that the joint report specify the matters which were agreed, the matters which were not agreed and the reasons for their not agreeing ("the joint report").
213 In section 4 of the joint report, the experts agreed that the ESA did not establish the level of contamination at the land. On its face, this aspect of the joint report demonstrates a breach by Mobil of the ESA obligations. However, it was submitted on behalf of Mobil that, on its proper construction, the ESA obligation required only that Mobil cause an ESA to be prepared which establishes, as far as reasonably practicable, the level of contamination at the land. In support of this submission, it was contended that the use of the words "to establish", rather than "which establishes", assists Mobil's submission. I reject this. In the context of the clause, the words "to establish" mean "for the purpose of establishing".
214 It was contended on behalf of Mobil that no ESA can conclusively establish the level of contamination at land. To do so would require all of the soil and groundwater to be sampled and analysed. This is an unrealistic commercial requirement. The parties could not have intended such an absolute requirement.
215 I accept that the parties did not intend that Mobil should test all of the soil and groundwater at the land. However, the degree to which the ESA required by cl. 7(b) must establish the level of contamination is not one based on some general notion of reasonableness. The extent to which an ESA required by cl. 7(b) must establish the level of contamination is that which will be sufficient to enable an assessment to be made as to whether any clean up is required under the clean up obligation so as to permit commercial uses under the applicable zoning. In this regard, it is convenient to set out the responses of the experts to the more general question as to whether the ESA "reasonably establishes" the level of contamination at the land:
"Peter Mirkov Response:
The scope of work that was prepared by Handex for the site assessment, under the existing service station use conditions, was in my opinion of adequate extent to 'reasonably establish' the type and magnitude of contamination at site.
Anthony Lane Response:
I disagree with Mr Mirkov because the Handex ESA of Dec 2000 fails to test soil evidently contaminated due to high PID readings, and the area of the USTs where significant contamination may be anticipated, has not been assessed to the extent possible and necessary to reasonably establish the level of contamination." (Emphasis added.)
216 Further, the experts were asked to express a joint opinion as to whether the sampling of soil and groundwater conducted by Handex, and recorded in the ESA, indicated that further testing at the land should have been undertaken to establish the level of contamination existing at 12 November 2000. The experts responded:
"Peter Mirkov Response:
As indicated previously no site assessment can 'establish' with total certainty the type and degree of contamination at a site. In my opinion the sampling of soil and groundwater as conducted at the site and recorded in the Handex report was of a reasonable scope to evaluate the likelihood of contamination being present at the site. A total of 15 bore holes were drilled at the site with 5 monitoring wells being installed in five of these boreholes. This is a greater scope of work by any industry standard for a typical service station than is often adopted. The drilling and sampling of soil and groundwater adjacent to USTs is not good practice and is in fact prohibited by safe work permitting practices, even the existing bores are closer to the USTs than advocated by safe work practices (ie closer than 8m).
Anthony Lane Response:
In my opinion further testing would have been required by November 2000 to reasonably establish the contamination levels by at least the following scope of work
1 Re-sampling and testing soil in the areas where high PID readings were obtained but soil not tested.
2. Sampling soil at four locations close to the USTs, under a site-specific safety plan for work in a hazard zone.
3. Installing a groundwater bore or GeoProbe implant in one of the soil bores close to the USTs." (Emphasis added.)
217 In my view, Mr Mirkov's responses are infected by the invalid tanks assumption and service station assumption. He was not entitled to make those assumptions. Further, both of the experts appear to have proceeded on the assumption that the ESA was required to be conducted with the tanks remaining on the land. As I have said, I reject this as a matter of contractual interpretation. If Mobil needed to remove the tanks in order to comply with its obligations under cl. 7(b) then it was required to do so. The fact that Mobil elected to leave the tanks at the land, and transfer ownership of them to the plaintiffs, cannot reduce the extent of either the ESA obligation or the clean up obligation.
218 In my opinion, the ESA did not comply with cl. 7(b). It was inadequate in its scope, design and implementation. The result was that the ESA does not enable a proper assessment to be made of the extent to which Mobil is required to clean up the land so as to permit commercial uses under the applicable zoning.
219 In the first place, the scope and design of the ESA was deficient because it was based upon the service station assumption. The scope and design of the ESA did not have any regard to the extent of the clean up obligation. As a result, the ESA specifically refers to, and assesses only, the suitability of the land for continuing use as a service station.
220 Secondly, the scope and design of the ESA was defective because it was based upon the tanks assumption. There was no consideration given to removal of the tanks. In my view, the ESA ought to have been designed on the assumption that the tanks would be removed, for the following reasons. First, the experts agreed that the most likely source of petroleum contamination at the land was the area immediately surrounding the tanks. This includes packing sands around the tanks, soil and groundwater. When Mobil's expert Mr Mirkov was asked about this, he gave the following evidence:
"Do you accept that having regard to the results which are known from the wells and bores which have been dug, that it is more likely than not that there would be some contamination around the tanks? --- One would assume that this is where the most likely source of the groundwater pollution has come from, but it is perplexing to find that the integrity test results that I have seen suggest that the tanks and lines are in fact tight as referred to in the industry, ie, having pressure tested and are not leaking. So although the tanks and/or lines are often the main source of groundwater contamination, it is not the only source. It could have been a bowser, it could have been an overfill, it could have been a range of other things, and I have seen numerous service stations where groundwater pollution was present and the tank pits were clean. Having said that, it is more likely that the tank pits will be contaminated than not, probably three times as likely or thereabouts, but we don't know. The tanks are still there, the backfill hasn't been tested and that is usually tested when the tanks are removed.
Your evidence about the likelihood is based on your extensive experience? --- Yes." (Emphasis added.)
221 Secondly, notwithstanding the fact that the area immediately surrounding the tanks is the most likely source of the contamination at the land, this area of the land could not be tested due to the continued presence of the tanks. It was not possible, because of safety concerns, to test the packing sands, soil and groundwater immediately surrounding the tanks. As a result, even though the ESA was designed to "target" the most likely sources of contamination, it did not do so, and the extent of contamination in the most likely area of contamination remains unknown.
222 Thirdly, the experts agreed that the only way to properly assess the level of contamination in and around the tank pit is to remove the tanks and then sample and test the sands, soil and groundwater in that immediate vicinity. If the tanks had been removed, there would have been nothing standing in the way of an ESA being prepared on the basis of soil bores drilled in a regular grid pattern across the whole of the land. Even if such a grid pattern form of sampling was used, it was the opinion of Mr Mirkov that:
"... you would still need to test the locations where the infrastructure was, so you would supplement a grid with some targeted sampling anyway."
223 In my view, this is what ought to have been done in this case. Having regard to the terms of the clean up obligation, Mobil ought not to have treated the ESA as one designed for the purposes of a lease hand back for continuing service station use.
224 Notwithstanding these matters, Mr Mirkov gave evidence that, in his opinion, the ESA adequately established the level of contamination at the land. However, this opinion was clearly based upon the invalid tank assumption and service station assumption. Both of these assumptions appear in Mr Mirkov's responses in the joint report, which I have referred to above. I reject Mr Mirkov's evidence on this issue.
225 Having regard to the finding I have made in relation to the inadequacy of the scope of the Handex ESA to establish the level of contamination at the site for ongoing commercial use, it is unnecessary to consider in detail the specific allegations raised by the plaintiffs in relation to deficiencies in the way the ESA was conducted by Handex. However, two specific allegations were raised and considered in great detail in the evidence. I will briefly consider these further matters.
226 First, the plaintiffs submit that Handex ought, at the least, to have taken soil samples when they installed the additional two groundwater monitoring wells in November 2000. The experts agreed that, if the objective of the ESA was to ascertain the level of contamination at the land in circumstances where there were indications of soil contamination at soil bores 5 and 6, Handex should have taken and tested soil samples when installing the additional groundwater monitoring wells in November 2000. Having regard to the fact that these wells were drilled in close proximity to soil bores 5 and 6, soil sampling at these locations would have assisted to further delineate the extent of the soil contamination in this area of the land.
227 Secondly, the plaintiffs allege that the ESA is deficient because Handex failed to send for analysis a sample of the soil taken from soil bore 5 at a depth of 5.1m. The PID reading of 1090 ppm at this location was the highest reading obtained by the Handex field testing. Mr Lane's evidence was that he could not understand why the sample had not been sent for analysis. This was particularly the case in circumstances where a soil sample taken at 2.5m depth from the soil bore nearest soil bore 5, soil bore 6, had disclosed a PID result of 950. This sample subsequently revealed, on a laboratory analysis, a concentration of benzene of 24mg/kg. On any view of the applicable investigation level, this was a very significant level of contamination which required further investigation and assessment.
228 Mr Hadwen was called by Mobil as a witness to support the sufficiency of the ESA.[33] Mr Hadwen is a consultant who at the time worked for Handex, although not on this particular ESA. He now works as an internal remediation manager for Mobil. Mr Hadwen said that he did not know why the sample from bore 5 was not sent for analysis because he had not spoken with the driller. Nevertheless, he offered two hypothetical explanations.
229 First, Mr Hadwen suggested that perhaps the driller had selected the two deepest samples from soil bore 5 at 5.5m and 6.1m in order to test whether the contamination had reached the groundwater table. Mr Lane's evidence was that this explanation did not sound plausible. While he acknowledged that it was relevant to establish whether the contamination has reached the water table, in Mr Lane's view it was most relevant to investigate the soil samples from soil bore 5 which revealed the highest PID readings. This was because groundwater naturally rises up and recedes through the soil. If the groundwater is contaminated it will deposit that contamination as it rises and recedes through the soil. This results in a "smear zone". The sample which Handex failed to test fell within this smear zone and, in Mr Lane's view, should have been sent to the laboratory for analysis. I accept this evidence.
230 Next, Mr Hadwen suggested that, in the course of the PID testing in the field, the integrity of the sample for laboratory analysis might have been destroyed so as to make it unsuitable for laboratory analysis. Mr Lane was of the view that it would be very poor field practice to use the entire sample for the PID test and not put a portion in a jar to go to the laboratory. He said that he would be "after someone's blood" if that happened on a job he was managing. I accept this evidence.
231 I find that the conduct of the ESA was flawed in the two respects discussed. The conduct of Handex in this regard was insufficiently rigorous to establish the level of contamination at the site.
232 The plaintiffs' case in relation to a breach of the ESA obligation focused on soil rather than groundwater. Nevertheless, it appears that the scope of the groundwater investigations conducted for the purposes of the Handex ESA were insufficient to establish the extent of the groundwater contamination at the site. As appears from the factual narrative which I have set out earlier in these reasons, the investigations following the service of the clean up notice revealed significant groundwater contamination issues. Were it not for the service of the clean up notice, I find that it is unlikely that these issues would have been fully revealed.
(3) Clause 7(b): Was Mobil obliged to clean up the land?
233 Many of the reasons which I have given for my finding that Mobil breached the ESA obligation are relevant to the allegation that Mobil breached the clean up obligation.
234 In the joint report, the experts expressed their opinions as to whether, in November 2000, the land was suitable for any as of right commercial use permitted under the applicable zoning. The experts did not agree. They responded:
"Peter Mirkov Response:
Based on the ESA data and on instructions that I received relating to responsibility for the underground storage systems being with the landowner and that Mobil has acceptance (sic) responsibility for groundwater management, I am of the opinion that the site was suitable for [commercial uses under the applicable zoning] as at 12 November 2000." (Emphasis added.)
Anthony Lane Response:
I disagree with Mr Mirkov and assert that the unacceptable risk indicated by the levels of contaminated soil in the vicinity of the UST pit in November 2000 make the site unsuitable for such use, at 12 November 2000, assuming contamination levels remain unchanged."
235 Further, in paragraph 5.6 of his expert report, Mr Mirkov demonstrated the significance of the tanks assumption to his opinions on this issue:
"The issue of any future construction over Underground Storage Tanks (USTs) must also be considered when evaluating future commercial land use. Clearly construction directly over USTs would not be structurally nor environmentally sound and as such the tanks and any immediately associated contamination would need to be removed prior to the construction of any such structures over these facilities. Furthermore, as detailed in the Blake Dawson Waldron letter of 29 September 2005 the tanks and associated infrastructure is not the property of Mobil and as such these facilities are not part of my assessment as they are the responsibility of other parties."
236 I do not accept the opinion of Mr Mirkov that the land was suitable for commercial uses under the applicable zoning. It is infected by the invalid tanks assumption. When the tanks assumption is put to one side, it is apparent that Mr Mirkov agrees with Mr Lane. I have set out above the evidence of Mr Mirkov to the effect that the most likely source of petroleum contamination at the land was the area immediately surrounding the tanks.
237 Mr Mirkov said that construction could not take place over the tanks because the tanks themselves posed a risk of explosion. This was so whether or not they were surrounded by contaminated packing sands, soil or groundwater. Mr Mirkov gave the following evidence in this regard:
"Another reason is that you wouldn't build it regardless whether there was contamination there or not because the tanks are there. You have a much more hazardous situation by building over the top of an explosive tank than anything to do with benzene being in soils. The presence of a tank that has petrol vapours in it is a much more hazardous situation than the possible presence of 24 milligrams of benzene in soil underneath the tank.
What could happen? --- It could explode, if it was struck and there was a spark.
So the likelihood is that in any underground storage tank which has been abandoned like this, there will be some petrol vapours left? --- You can't get rid of all of them. They put in some pumps and things like that, but there is always some petrol left in the tanks."
238 I have found, in the factual narrative above, that Mobil took no steps to decommission the tanks in accordance with cl. 4(b) of the lease. Based on this, I find that it is more likely than not that there was, at least, some residue of petroleum products in the tanks at the time Mobil vacated the land on the expiry of the lease.
239 In my view, it follows that Mobil was required to remove the tanks in order to comply with the clean up obligation. The continued presence of the tanks at the land constituted contamination at the land which prevented the construction, in the vicinity of the tanks, of a commercial building to be used for commercial uses permitted by the applicable zoning. By leaving the tanks at the land, Mobil breached the clean up obligation.
240 Furthermore, I find that Mobil was also in breach of the clean up obligation with respect to the "hotspot" of contamination located at soil bore 6. The ESA recorded a soil concentration of benzene of 24mg/kg at 2.5m depth from this soil bore. Mr Mirkov was asked whether the hotspot could, of itself, cause a danger to a construction worker who may be exposed to the soil in that area of the land during construction works. In response, Mr Mirkov said that it would depend upon "how extensive" the contamination was in this area of the land. He accepted that the ESA did not disclose the extent of the contamination in this area of the land.[34]
241 In further questioning on this issue, Mr Mirkov gave the following evidence:
"Two things to consider there, first of all, the contamination is at greater than 2.5m depth, so the likelihood of any shallow excavations encountering it are minimised...
Secondly, the presence of this does not preclude the land being used for the purposes we discussed, it may require management plans to be implemented during construction works, and this is very common when statutory audits are done... for example, the entire Docklands area has various EPA and auditor imposed caveats that say once you get to two metre depth you must enact an earthworks management plan, so the contractors who are working in those areas are protected because it is known that there could be some risks to them if they were to dig deeper, and the management plans require them to follow certain processes. So it is not a case of ignoring it, it is a case of management plans being put in place to prevent exposure. It is quite common.
So absent such a management plan, if there was construction on the site there is a risk of there being harmful exposure to a construction worker, is that the case? --- That is possible, yes. If there were no management plan put in place.
Are you aware of any management plan in respect of soil being put in place or recommended? --- Well, not that I am aware of on this site, no."
242 Later, Mr Mirkov was asked what the plaintiffs, as owners of the land acting responsibly, would do if they wished to develop it themselves and build a commercial building. He gave the following evidence:
"Assume they are not selling it, they are going to build on it themselves? --- They would engage a consultant and they would write an environmental management plan.
And that would cost money? --- Yes, it would cost some money to write an environmental management plan, and that plan would stipulate things like once you get to two metres a consultant should be brought to the site with a PID meter or some other device to sample and test the soil to see if indeed it is contaminated, if indeed it does pose an exposure problem to the workers.
...
And depending on the level, or the extent of the contamination found, there may be removal of some soil required or remediation of some soil? --- That's right, it depends on the nature of this hotspot... but the point of the plan would be to ensure that once you started to dig past that point you would have means to monitor, measure and test, so that you could respond appropriately."
243 I find that this evidence of Mr Mirkov is, by itself, sufficient to establish a breach by Mobil of the clean up obligation. If the plaintiffs wished to develop the land by constructing on it a commercial building, perhaps including an underground carpark, to be used for one of the commercial uses permitted by the applicable zoning, the plaintiffs would have been put to the inconvenience and expense of employing an environmental consultant to write an environmental management plan to deal with the contamination disclosed by the ESA, at least in the area of soil bore 6. Further, if such construction was over the area of the tanks, where the experts agree there is likely to be further contamination, I find that it is likely that the environmental management plan would need to address the likely contamination in this area.
244 In my opinion, the clean up obligation required Mobil to return the land to the plaintiffs in a state which would enable the plaintiffs to develop the land for any of the commercial uses permitted by the applicable zoning. Mobil did not do so because the plaintiffs could not do this without incurring the cost and inconvenience of engaging an environmental consultant to write an environmental management plan.
245 As a further ground establishing a breach of the clean up obligation, the plaintiffs placed reliance upon the risk assessment conducted by Mr Lane with respect to the hotspot of contamination at soil bore 6.
246 Mr Lane's assessment was that this concentration of benzene posed a lifetime cancer risk to an office worker in a commercial building built over that hotspot. On this basis, Mr Lane was of the view that the site was not suitable for any as of right ongoing commercial use as at November 2000.
247 Mr Lane conducted an assessment of the lifetime risk to an office worker in a commercial office building built on this site from the presence of the levels of soil contamination disclosed in the ESA. Mr Lane and his associates undertook this risk assessment using a modelling software package known as "RISC 4". Using this model, Mr Lane measured the risk to human health of exposure in an office environment to the vapours released by the level of benzene found at soil bore 6. This risk assessment was based on exposure for eight hours a day for between 25 and 30 years. Mr Lane calculated the incremental lifetime cancer risk from exposure to contaminated soil at the site as ranging from 1.2 x 10-5 to 2.8 x 10-5. This is above the adopted acceptable risk level of 1x 10-5.
248 Mr Mirkov criticised the results arrived at by Mr Lane in his modelling of the lifetime cancer risk posed by the vapours from the benzene contamination at soil bore 6. Mr Mirkov made three principal criticisms of Mr Lane's modelling:
(1) The presumed number of 12 air changes per day was too low. He said that this number was the default standard in the "RISC 4" software for residential use. A more appropriate figure would have been 48 air changes per day for commercial use.
(2) It was inappropriate to conduct the risk assessment on only the highest result of 24mg/kg of benzene at soil bore 6. Instead, the contamination should be averaged out over the whole of the land that a commercial building over the area of soil bore 6 would occupy.
(3) When the overall descriptions of the soil type from all 15 boring logs were taken into account, the general profile at the site was clay, not silt or sand as assumed by Mr Lane in his modelling. Again, Mr Mirkov's opinion was that the proper approach was to conduct the risk assessment on the basis of the average conditions over the whole of the site to be occupied by the building.
249 Mr Mirkov did not himself conduct a site specific assessment of the risks to human health from commercial use of the land. He confined himself to criticising the assessment by Mr Lane.
250 I am not satisfied that Mr Mirkov cast any serious doubt over the methodology employed by Mr Lane in conducting the risk assessment. In particular, I accept Mr Lane's evidence that it is more appropriate to act conservatively by conducting a risk assessment in relation to benzene by reference to the highest concentration found; and by reference to the soil type at that particular location. This approach is logically preferable to averaging out the soil type and concentrations of contamination across the entire site. When the precise future use of the site is unknown, it appears to me to be appropriately conservative to identify the risk posed by particular locations on the site, rather than the average risk.
251 Mr Lane's evidence as to the need to act conservatively when considering the risks posed by contamination with a known carcinogen such as benzene is supported by Schedule B(4) of NEPM 1999, where it is stated that the key principles in assessing risk include:
"• The primary aims of risk assessment are to protect public health and the environment, putting these responsibilities before all other considerations.
......
• To protect public health and environment an appropriate degree of conservatism must be adopted to guard against uncertainties."
252 Perhaps the most fundamental criticism by Mr Mirkov of Mr Lane's risk assessment was that it was based on an incorrect assumption as to the number of air changes per day. It was submitted that the computer model should have been run on the assumption that there would be 48 air changes per day. However, this submission was based upon an underlying premise that the hypothetical office worker in the commercial building would be present for 24 hours a day. Mr Lane's risk assessment assumed exposure for an eight hour working day. I find that this was a reasonable assumption. Based on this assumption, Mr Lane accepted that it would be appropriate to assume two air changes per hour in modelling the risk. This would result in an assumption of 16 air changes per day being appropriate. Mr Lane said, in this regard, that the difference between 12 and 16 air changes per hour "is not that significant". Mobil called no evidence as to what the results of the computer modelled risk assessment would have been if 16 air changes had been assumed. I accept Mr Lane's evidence that the difference is unlikely to have been significant. Accordingly, another breach of the clean up obligation is established.
NUISANCE CLAIM
253 As an alternative to their claim in breach of contract, the plaintiffs raised a claim against Mobil based on the tort of nuisance. The plaintiffs' submissions concerning this claim were briefly put in writing and not developed to any extent in oral argument. The written argument filed on behalf of Mobil did not deal with the nuisance claim at all. In oral submission, it was submitted on behalf of Mobil that the case had been conducted on the basis of breach of contract and that no evidence had been led to prove that the contamination existing at the land was the result of the conduct of Mobil. It was submitted on behalf of Mobil that the evidence established that the land had been used for a petrol station prior to it taking occupation in 1981.
254 As appears above, the location of the contamination at the land, in the vicinity of the petrol bowsers and tanks, indicates that it is the conduct of Mobil which has caused all or a substantial part of the contamination existing at the land. Based on the duration of Mobil's possession of the land and conduct of a petrol station business on it, I infer that this is so.
255 However, as the matter was not fully argued and I have concluded that the claim in contract is made out, it is unnecessary for me to reach a conclusion as to whether the tort of nuisance has been established.
CAUSATION ISSUES
256 It was submitted on behalf of Mobil that there was no causal link between any loss suffered by the plaintiffs and any breach of the lease by it. The basis of this submission was that the proposed lease to Woolworths did not proceed because of conduct on the part of the plaintiffs which had the effect of breaking the chain of causation between any breach of the lease and the failure to secure Woolworths as a tenant.
257 The conduct of the plaintiffs which it was contended had this result was two-fold. First, reliance was placed upon the contention that, at the 20 March 2001 meeting, Mr Flicker refused the Mobil tanks offer. Secondly, reliance was placed upon the refusal by the plaintiffs to accept the Woolworths tanks offer.
258 I reject the submissions made on behalf of Mobil in this regard. In my view, the conduct referred to did not operate to sever any causal connection between the breaches of cl. 7 by Mobil and the failure of the proposed lease to Woolworths to proceed. Further and in any event, the claims made by the plaintiffs do not depend entirely upon proof of a causal connection between the breach by Mobil and the failure of the proposed lease to Woolworths. Whether or not the lease to Woolworths proceeded, the fact remains that the land was, by reason of the breaches by Mobil, contaminated to a level which made it unsuitable for commercial uses under the applicable zoning. Unless and until Mobil remedied its breaches, the plaintiffs were unable to use the land for the commercial uses contemplated by cl. 7(b) of the lease. In these circumstances, the licence fee was payable.
259 As to the Mobil tanks offer, I have found that it did not amount to a formal offer but was merely part of the discussion about ways in which the dispute between the parties might be progressed or resolved. But even if it was a formal offer, it did not go far enough to sever any causal connection between the breaches of cl. 7 by Mobil and the failure of the plaintiffs to secure the proposed lease to Woolworths. The offer made no reference to the clean up of any contaminated soil or groundwater at the land, whether surrounding the tanks or elsewhere (such as at soil bore 6). Further, the offer did not include an offer to "make good", as required by cl. 7(d). In my view, given that the tanks were by this time the property of the plaintiffs, Mobil was required to re-install or replace the tanks if it removed them in the course of performing its clean up obligation. This was required by Mobil as part of the make good obligation. If the plaintiffs had refused an offer which included all of these elements, the position may have been different. But no such offer was ever made by Mobil.
260 As to the refusal by the plaintiffs of the Woolworths tanks offer, this offer was inextricably linked with the requirement by Woolworths that it would not lease the land unless and until the contamination was cleaned up to its satisfaction, as required by the Landlord's Works requirement. It was only if the clean up required the removal of the tanks that there was an issue. By making the Woolworths tanks offer, Woolworths was seeking to ensure that it would be able to proceed with the proposed lease even if the tanks needed to be removed as part of the clean up process. The refusal of the Woolworths tanks offer did not cause Woolworths to lose interest in the property. I am satisfied that the plaintiffs and Woolworths would have reached some agreement about the tanks if they were removed by Mobil in the course of complying with the clean up obligation. I will return to this issue later in this judgment when considering the amount of the plaintiffs' loss.
261 I find that the breaches by Mobil of the lease are to be regarded, on a commonsense view, as the cause of the plaintiffs failure to secure final agreement with Woolworths on a lease. Alternatively, at the very least Mobil's breaches caused the plaintiffs to lose a substantial opportunity to lease the land to Woolworths.
MITIGATION ISSUES
262 As an alternative to the contention that the conduct of the plaintiffs severed the chain of causation, it was submitted on behalf of Mobil that such conduct on the part of the plaintiffs amounted to a failure by the plaintiffs to take steps which they ought reasonably to have taken so as to minimise their loss. I reject this submission. For the reasons given above in respect of causation issues, there was nothing unreasonable in the plaintiffs refusing to accept the Mobil tanks offer. The Mobil tanks offer fell far short of an offer by Mobil to comply with the clean up obligation.
263 Nor can the conduct of the plaintiffs in respect of the Woolworths tanks offer be considered unreasonable. The plaintiffs acted at all times on the basis of the expert advice of Mr Diomides. The substance of that advice was confirmed by Mr Crockett and Ms Mazur. In circumstances where Mobil was refusing to carry out any clean up, and in the absence of any offer by Mobil to replace the tanks if they were removed as part of any clean up, it was, in my view, reasonable for the plaintiffs to wait and see what action Mobil took as a result of the matter being referred to the EPA before committing itself to the Woolworths tanks offer.
264 In this regard, Mobil knew, or had at least prepared internal estimates, of the cost of clean up of the land to permit commercial uses. Mobil's estimate of that cost was approximately $130,000 and was prepared within a few days of the ESA being completed and provided to the plaintiffs. Notwithstanding this knowledge, Mobil did not communicate it to the plaintiffs. Mobil continued throughout the dispute to leave the plaintiffs in the dark, to do the best that they could on the basis of the advice from the experts retained by them. As I have said, I accept the evidence of Mr Flicker that he was told by Mr Diomides that the costs of cleaning up the land were "very difficult to establish" because the extent of the contamination was unknown. Further Mr Diomides told Mr Flicker that the clean up costs could be very substantial, perhaps as much as $1M or more. In these circumstances, it was not unreasonable for the plaintiffs to insist upon Mobil performing its contractual obligations before exposing themselves to obligations to clean up the contamination at the land or to replace the tanks in the event that they were removed as part of any clean up.
265 The allegation by Mobil that the plaintiffs failed to act reasonably to mitigate their loss and damage is wholly unmeritorious. Mobil is one of the largest petroleum retailers in the world. It has vast resources and access to both internal and external expertise on the issue of petroleum contamination of land. In its dealings with the plaintiffs, it was Mobil who acted unreasonably. It commissioned the ESA on the false premises of the tanks assumption and the service station assumption. When the Mobil officers responsible for the conduct of the matter became aware of the requirements of cl. 7(b) as to ongoing use, they did not change their approach. They continued to assert, in answer to the plaintiffs' complaints, that the land was suitable for ongoing use as a service station and that there was, accordingly, no clean up obligation upon Mobil. It is not to the point that Mobil knew by this time that the plaintiffs wished to lease the land to Woolworths for use as a service station. That intention could always change, as this case demonstrates. It was the obligation of Mobil to comply with the terms of cl. 7(b) whatever may have been the current intentions of the plaintiffs for the future use of the land. As I have said, Mobil did not do so and it does not lie in its mouth to assert that the plaintiffs acted unreasonably.
ASSESSMENT OF DAMAGES
(1) Relevant legal principles and issues
266 The claim of the plaintiffs for breach of contract brings into operation the ordinary rule as stated by Parke B in Robinson v Harman[35]:
"that where a party sustains a loss by reason of a breach of contract, he is, so far as money can do it, to be placed in the same situation, with respect to damages, as if the contract had been performed."
This statement of principle has been applied and accepted in Australia.[36]
267 Where a plaintiff suing for breach of contract has been deprived of the opportunity to enter into a second contract, damages are recoverable for the lost opportunity, provided that the prospect of the second contract occurring is "sufficiently substantial to stamp it as a real commercial advantage."[37]
268 It was accepted by Mobil that, if the plaintiffs established a breach by Mobil of the clean up obligation and that this breach caused the plaintiffs to lose the opportunity to lease the land to Woolworths, such opportunity was sufficiently substantial to be compensable. However, it was submitted on behalf of Mobil that the opportunity to secure a lease to Woolworths was not a certain opportunity. Accordingly, the plaintiffs' damages should be assessed by reference to the Court's assessment of the prospect of the plaintiffs leasing the land to Woolworths if Mobil had complied with the clean up obligation. In this regard, Mobil placed reliance upon the statements of principle in Sellars v Adelaide Petroleum[38] and Commonwealth v Amann Aviation Pty Ltd.[39]
269 In Amann Aviation[40], Brennan J stated the principle in the following terms:
"The relevant principle is that when performance of a contract by a defendant (including the permitting of the plaintiff to perform his obligations under the contract) would have resulted in the plaintiff's acquiring a particular commercial advantage but the advantage is lost by reason of the defendant's breach, the loss of the advantage is compensable and its value is to be taken into account in assessing a plaintiff's damages. If the advantage in question is a certain opportunity to secure a profitable second contract, the profits of the second contract can be recovered. Such an advantage is worth more than a merely preferential chance of securing such a contract but such a chance, like the chance in Chaplin v Hicks, has a value and the loss of the chance is a proper subject of compensatory damages.
However, to attribute a value to such a chance the court might have to engage in a degree of speculation, speculating as to the likelihood that a profitable contract would be available, what the likely profits would be and the likelihood that the plaintiff would secure the contract against competition by others."
270 In Sellars[41] Mason CJ, Dawson, Toohey and Gaudron JJ stated that the principle allowing recovery of damages for deprivation of a commercial opportunity:
"... should be ascertained by reference to the court's assessment of the prospects of success of that opportunity had it been pursued."
271 In Sellars[42] Brennan J stated:
"Provided an opportunity offers a substantial, and not merely speculative, prospect of acquiring a benefit that the plaintiff sought to acquire or of avoiding a detriment that the plaintiff sought to avoid, the opportunity can be held to be valuable."
272 There was no dispute about the applicable legal principles. It was submitted on behalf of the plaintiffs that the opportunity which it had lost was "a certain opportunity to secure a profitable second contract",[43] so that damages should be assessed on the basis that the plaintiffs have been deprived of the whole of the benefit of the proposed lease to Woolworths.
273 The Court's assessment as to the value of the lost opportunity to lease the land to Woolworths is capable of being relevant at two levels. This is because there are two limbs to the plaintiffs' damages claim. First, the plaintiffs seek as damages either the amount of rent which Woolworths would have paid under a lease prior to the sale of the land in November 2004 or the amount of licence fees payable by Mobil under cl. 7(d) of the lease for the period between the expiration of the lease and the sale of the land in November 2004. The quantum of these two alternative claims is, if a lease to Woolworths is treated as a certainty, almost identical. However, if the Court assesses the lost opportunity to lease the land to Woolworths as less than certain, then damages for loss of rent could be significantly less than the claim for licence fees. Furthermore, as the licence fees are amounts accruing due under the terms of cl. 7(d) of the lease, a judgment for the plaintiffs based on non-payment of licence fees may give the plaintiffs a higher entitlement to interest on its damages award. This is because the plaintiffs have consistently made demand for licence fees from an early time.[44] Having regard to these matters, in the event of success on their claims the plaintiffs have elected to have a judgment under cl. 7(d) of the lease. It follows that the Court's assessment of the prospect of a lease being concluded with Woolworths if Mobil had complied with its clean up obligation under cl. 7(d) is not relevant to the first limb of the plaintiffs' claims.
274 However, the position is not so straightforward with respect to the second limb of the plaintiffs' claim. Under this limb, the plaintiffs claim as damages the difference between the actual sale price obtained by them on sale of the land in November 2004 and the sale price which it is alleged could have been obtained if Mobil had complied with the clean up obligation. The Court's assessment of the prospect that the plaintiffs would have secured a lease to Woolworths, and on what terms, is relevant to this limb of the damages claim.
(2) Loss of rent/licence fees
275 As I have said, on the first limb of their claim the plaintiffs have already elected for a remedy calculated by reference to cl. 7(d) of the lease. Accordingly, there being no dispute as to the arithmetic, there will be judgment for the plaintiffs in the sum of $575,735.99 and interest. As to the calculation of interest, upon which I will hear the parties further if no agreement is reached, I note that the plaintiffs have demanded payment of licence fees from an early time.
276 By a letter dated 28 December 2000, Mr West informed Mr Burge of Mobil:
"In accordance with clause 7(d) of the Lease, the Landlords require the continuing payment of rent until the Lease is complied with."
277 Mr Burge understood this as a claim by the plaintiffs for the licence fee referred to in cl. 7(d) of the lease, which is equivalent to the rental payable under the lease at the date of its expiration. At regular intervals from this time, the plaintiffs, through Mr West, continually demanded from Mobil that it pay the licence fee until the land was cleaned up in accordance with cl. 7(b) of the lease. In future correspondence, there was no confusion as to the description of the licence fee, and it was so described in the demands made.
(3) Diminution in value of the land
278 The parties each called one expert valuer to give evidence. Their opinions were diametrically opposed on all but one issue. The experts agreed that, if the land was valued on the basis that it was leased to Woolworths on commercial terms, the fair market value of the land could be ascertained by applying a capitalisation rate of 8 per cent on the passing rent. On this basis, if the passing rent was taken as being in accordance with the rent which would have been payable by Woolworths under the proposed lease, without any adjustment by reason of a need to install new tanks, a value of $1,870,000 is established.
279 However, if I am to consider valuation of the land on the basis that it was leased to Woolworths, it is in my view appropriate that I consider and make findings on two matters. First, as to the likely commercial terms which would have been agreed between the plaintiffs and Woolworths if Mobil had complied with the clean up obligation. This is necessary to identify the opportunity which has been lost. Secondly, I will proceed to assess the prospect of whether a lease to Woolworths on those terms would have proceeded at all.
280 In considering these questions, a number of matters must be taken into account. In my view, the principal factors to be considered are:
(1) What was the extent of the interest of Woolworths in leasing the land?
(2) To what standard was Mobil required to clean up the land?
(3) Within what time was Mobil required to clean up the land?
(4) To what standard did Woolworths require the land to be cleaned up?
(5) Would the commercial terms of a lease to Woolworths have remained the same if Mobil removed the tanks?
(6) What were the uncertainties which might have caused Woolworths to refuse to lease the land?
I will consider each of these factors separately.
281 As to the extent of Woolworths' interest in leasing the land, I find that it was extremely high. The evidence of this has been set out in the factual narrative contained in this judgment. In summary, Woolworths was at the time expanding its chain of petroleum retail outlets at a rapid pace, described by Mr Webb as "go, go, go, go". The extent of Woolworths' interest is indicated by the fact that, notwithstanding the contamination issues at the property, Woolworths remained interested in leasing the land until at least January 2002. This was more than one year after the expiration of the lease and the agreement, subject to contract, of the commercial terms of the proposed lease.
282 As to the standard of clean up, I have held that Mobil was required to clean up the contamination at the land so as to enable it to be used for the commercial uses permitted under the applicable zoning. I have found that the clean up obligation extended to the removal of the tanks, cleaning up any contamination such as that found in soil bore 6 and in the vicinity of the tanks and then, under the make good obligation, re-installing or replacing the tanks or tanks of at least similar quality.
283 As to the time within which Mobil was required to clean up, cl. 7 of the lease makes it abundantly clear that Mobil could not take its time. Clause 7(b) requires an ESA to be prepared "at the expiration" of the lease and that Mobil "shall thereupon" clean up the land. Clause 7(d) provides that Mobil is to have access to the land for a period of 30 days following the expiration of the lease "or such longer period as is reasonably required" (emphasis added). Such access is for the purpose of carrying out the clean up works and to "then make good any damage caused by such works to the reasonable satisfaction of [the plaintiffs]". Until Mobil has complied with all of these obligations, Mobil is obliged under cl. 7(d) to pay the licence fee. All of these factors, together with commercial commonsense, indicate that Mobil was required to clean up the land within a reasonable time of the expiration of the lease. In this regard, a reasonable time must take account of the right of the plaintiffs to utilise the land as soon as reasonably practicable for the commercial uses permitted by the applicable zoning.
284 The evidence of Mr Samardjiev is relevant to the reasonable time required to perform clean up works at the land. Mr Samardjiev gave evidence that he was aiming to get permits for the demolition of all buildings on the land and to clean up the contamination, including removing the tanks, in time to allow United Petroleum to install its own tanks, backfill and compact the soil and redevelop the land for the purpose of commencing trading in about February 2006. At the earliest, Mr Samardjiev's efforts in this regard could have commenced in early October 2005. The evidence of Mr Samardjiev supports a finding that it was possible for all of these works to be carried out within a period of four months. I find that a reasonable time for Mobil to comply with the clean up obligation and the make good obligation was no more than six months after the expiry of the lease. This allows, in order to cater for contingencies, a further two months in addition to the timeframe against which Mr Samardjiev said he was working to satisfy the requirements of United Petroleum. Accordingly, the clean up and make good obligations of Mobil should have been complied with by 13 May 2001 at the latest.
285 There is evidence as to the standard to which Woolworths required the land to be cleaned up. That standard is to be found in the Landlord's Works referred to in cl. 2.3 of the schedule to the draft agreement for lease. Clause 2.3(b) of that schedule provided that the plaintiffs were required to remove or procure:
"... the removal of all contamination from the [land] and remedying or procuring the remedying of all breaches of Environmental Laws[45] in respect of the [land] so that the level of contamination at the [land] is in accordance with the Environment Protection Authority Victoria guidelines for the level of contamination at premises of the nature of the [land] and the requirements of all Australian Authorities and so that there are no breaches of Environmental Laws in respect of the [land]." (Emphasis added.)
286 In my view, the standard of clean up required by Woolworths was no higher than the clean up obligation. Although the term "Environmental Laws" is widely defined, I do not think that this alters the situation. Woolworths were very keen to lease the land, and it is unlikely that any strict interpretation of "Environmental Laws" on its part would have caused it to withdraw from the proposed lease if Mobil had complied with its clean up obligations. In particular, I note that the standard of clean up required by Woolworths was "in accordance with the [EPA] guidelines for the level of contamination at premises of the nature of the [land]". The reference to premises of the nature of the land, indicates that the extent of clean up required by Woolworths was so as to permit the land to be used for a service station. That was its immediately preceding use and was the proposed use by Woolworths. Accordingly, the standard of clean up required by Woolworths was of a lesser extent than that required to be done by Mobil to comply with the clean up obligation.
287 Further, under cll. 2.3(f) and (g) of the schedule to the draft agreement for lease, Woolworths required that the tanks remain at the land and be in working order and free of leaks and other defects. As I have said, having regard to the fact that Mobil assigned ownership of the tanks to the plaintiffs, Mobil was required to reinstall or replace them in accordance with its make good obligation under cl. 7(d). Had it done so, a question arises as to whether this would have satisfied Woolworths, or whether it would have sought to alter the commercial terms of the proposed lease.
288 On the one hand, Mobil cannot be heard to say that the tanks were not in working order and free of defects, as required by Woolworths. Mobil asserted throughout the trial that the tanks had been tested and found to be "tight" and, in final submissions, maintained the submission that I should find that the tanks were in fact "tight" at the expiration of the lease.
289 On the other hand, the removal of the tanks by Mobil would have provided Woolworths with an opportunity to insist upon new tanks being installed by the plaintiffs. On no view of the make good obligation, could Mobil have been required to pay for the cost of installing new tanks.
290 In this regard, it must be remembered that the tanks were over 20 years old and were made of steel. Corrosion was likely. Later in the day of the 20 March 2001 meeting, Mr Webb telephoned Mr Diomides. Mr Diomides' telephone log records the following conversation:
"20/3/01 Steve Webb rang late pm after meeting. I advised him of discussions at subsequent meeting with site owner and that tanks may be 20 to 25 years old and may need to be replaced. Mobil took option of giving USTs to site owner but toward end of meeting offered to remove tanks if owner prefers. Steve Webb indicated that Woolworths want to be leasing a compete (sic) service station with viable tanks. 'Positive tank test today may result in negative result tomorrow.'"
291 I find that it is probable that, as a result of Mobil removing the tanks in order to comply with the clean up obligation, there would have been a renegotiation of the commercial terms of the proposed lease to Woolworths. Although it occurred after the six month period within which I have found Mobil was obliged to comply with the clean up and make good obligations, the evidence establishes that, when the issue of possible removal of the tanks was raised by the plaintiffs,[46] Woolworths responded seeking compensation.[47] Soon after, Woolworths made the Woolworths tanks offer.[48] The response of the plaintiffs was to continue to insist that, if the tanks were removed during clean up works, the plaintiffs and Woolworths could renegotiate the commercial terms.
292 I find on the balance of probabilities that, upon Mobil removing the tanks as part of the clean up works, it is more probable than not that the plaintiffs and Woolworths would have reached agreement on revised commercial terms. The effect of that agreement would most likely have been to impose the cost of installing new tanks on the plaintiffs. This could have been done by the plaintiffs agreeing to pay for the installation of new tanks, or by agreement being reached as to a revised rental, such as that contemplated by the Woolworths tanks offer. Accordingly it is necessary to take this likelihood into account in considering the value of the opportunity which has been lost by the plaintiff.
293 Whether that agreement would have involved the plaintiffs paying for the new tanks or Woolworths paying a reduced rental is a matter of speculation. However, the fact that the plaintiffs rejected the Woolworths tanks offer indicates that they were not disposed to accept a reduced rental which involved Woolworths seeking to recoup the cost of the tanks, and interest thereon, over the 15 year period of the lease. In my view, it is most likely that the plaintiffs would have elected to pay for the cost of new tanks, rather than accept a reduced rental.
294 The Woolworths tanks offer involved a reduction of the annual rent by 9 per cent of the cost of installation of new tanks. The only credible evidence as to the cost of installation of new tanks was an internal Woolworths' estimate of $250,000.[49] It appears that the Woolworths tanks offer was based upon this estimate, and would have had the effect of Woolworths recouping the cost of the tanks, together with a margin for interest, over a 15 year period. On my calculations, the Woolworths tanks offer involved an annual rent reduction of $22,500 over 15 years.[50] This would have involved the plaintiffs in receiving $337,500 less rent over this period.
295 Accordingly, I am of the opinion that the value of the land should, for the purposes of the second limb of the plaintiffs' damages claim, be assessed on the basis that the Woolworths lease was in place on the commercial terms agreed between the plaintiffs and Woolworths in November 2000. As I have said, on this assumption, there is no dispute between the experts as to the appropriate capitalisation rate to apply to the passing rent. The result is that, for the purposes of considering the second limb of the damages claim, I will adopt a value for the land in November 2004 of $1,870,000. This exceeds the sale price to United Petroleum by $669,000. However, the sum of $250,000 for the cost of new tanks must be deducted from this amount, leaving a total of $419,000.
296 I have no doubt that Mr Flicker would have attempted to obtain from Mobil a contribution towards the cost of new tanks at the land. However, I am not satisfied that there is any realistic possibility that Mobil would have agreed to contribute any amount towards the purchase of new tanks. It was not obliged to do so and its conduct throughout the dispute indicates that it would have been most unlikely to make any payment which it was not legally obliged to make.
297 There remains for consideration my assessment of the prospect that the Woolworths' lease would not have proceeded at all. After all, the draft agreement for lease was never signed and the issue concerning compensation to Woolworths for the cost of new tanks may have proven a sticking point which could not be resolved by negotiation. However, in assessing the value of the opportunity which has been lost, I have already assumed against the plaintiffs that they would have been required to pay for new tanks if a lease to Woolworths was to proceed. Accordingly, it is not in my view appropriate that I further discount the plaintiffs' damages by reason of this contingency.
298 The question remains as to whether I should nevertheless reduce the damages because of the prospect that, for some other reason, the proposed lease to Woolworths might not proceed. In this regard, I note that in final written submissions Mobil relied upon "two possible reasons for the lease to Woolworths not proceeding". First, it was submitted by Mobil that Woolworths may have withdrawn from the proposed lease because of the state of contamination of the land. Mobil accepted that, if it was in breach of the clean up obligation, it was responsible for, and could not rely upon, this contingency. Secondly, it was submitted on behalf of Mobil that Woolworths may have withdrawn because there was no agreement between the plaintiffs and Woolworths as to the financial consequences if the tanks were removed as part of the clean up of the land. As I have said, I have taken this matter into account in assessing the value of the opportunity which the plaintiffs have lost. It seems to me that it would be doubly penalising the plaintiffs if I were to take this matter into account further in assessing the prospect that the lease to Woolworths might not have proceeded at all.
299 However, the fact remains that the draft agreement for lease was never signed. There are no certainties in commercial life. Although Woolworths was extremely keen to lease the land, it was open to it to change its mind. It seems to me that I should make a small reduction to the damages recoverable by the plaintiffs to take account of this general commercial risk. In doing so, I take account also of the impression which I gained from the evidence, and from observing Mr Flicker in the witness box, that he is a man who drives a hard bargain, and this may have resulted in Woolworths refusing to proceed. Accordingly, I will further reduce the damages by an amount of 10 per cent to take account of this possibility. This will have the effect of reducing the plaintiffs' damages for diminution in the value of the land by a further $41,900, leaving a figure of $378,900.
300 The plaintiffs put their claim for damages for diminution in the value of the land on an alternative basis. It was submitted on behalf of the plaintiffs that, if the land was valued in November 2004 on the basis of vacant possession, a value of $1,810,000 would be applicable. If this value were to be adopted, the plaintiffs' damages on this account may be considerably larger than I have found. However, I would still need to consider whether another tenant could be found on the same commercial terms as if the Woolworths' lease had proceeded and, in that regard, to have given consideration to the state of the tanks. Although Mobil may have been required to reinstall the existing tanks as part of its make good obligation, or to replace them with tanks of a similar age which tested as "tight", I am not satisfied that another petroleum retailer would have agreed to lease the land for 15 years, at the same rent which Woolworths agreed to pay, with tanks in that condition.
301 In any event, the plaintiffs do not have a right to elect the basis upon which damages will be assessed. It is a matter for the Court to determine the correct measure of damage, on the basis that the plaintiffs are to be put in the position they would have been had the contract been performed.[51] Given my view that, if Mobil had performed the clean up obligation, the plaintiffs would have leased the land to Woolworths on the revised commercial terms discussed above, it is inappropriate to assess damages on the basis that the Woolworths' lease did not proceed. Indeed, this would be contrary to the whole tenor of the plaintiffs' case, which was that it has been deprived of the opportunity to lease the land to Woolworths.
302 It is accordingly unnecessary for me to consider the conflict in the evidence of the expert valuers as to the value of the land in November 2004 if it was sold with vacant possession.
(4) Conclusions on amount of damages
303 As stated above, the plaintiffs are entitled to recover:
(1) a liquidated amount of $575,735.99 for licence fees due under cl. 7(d) of the lease; and
(2) in respect of diminution in the value of the land, the sum of $378,900 as damages for breach of the clean up obligation under cl. 7(b) of the lease.
These amounts total $954,635.99. There will be judgment for the plaintiffs for this amount, together with interest.
304 I will hear the parties as to interest and costs.
[1] A reference to Mobil Oil Australia.
[2] This reference to "this clause 2.3(d)" is, in my view, an error and was intended to be a reference to "clause 2.3(b)".
[3] Qualitative Risk Assessment.
[4] Groundwater Monitoring Event.
[5] It appears that Ms Mazur saw the penultimate draft of this report.
[6] Supreme Court (General Civil Procedure) Rules 1996 (Vic) r 29.15.
[7] E-mails dated 21 and 27 October 2005 and 2 and 4 November 2005 between Mr Samardjiev and Elias Anastasiou of United Petroleum.
[8] A reference to this proceeding.
[9] Dovuro Pty Ltd v Wilkins [2003] HCA 51; (2003) 215 CLR 317 at [25] per Gleeson CJ, [66]-[71] per Gummow J.
[10] No application was made for an adjournment of the trial pending the completion of Mobil's proposed clean up works and the gathering of evidence in connection with those works being undertaken.
[11] [2005] VSC 347 at [88] to [94]; see also Patrick Corporation Ltd v Toll Holdings Ltd [2005] VSC 392 at [81] to [87] per Dodds-Streeton J.
[12] Reardon Smith Line Ltd v Ynngar Hansen-Tangen [1976] 1 WLR 989 at 997; Codelfa Construction Pty Ltd v State Rail Authority of New South Wales [1982] HCA 24; (1982) 149 CLR 337.
[13] [1932] UKHL 2; [1932] All ER 494.
[14] [1932] UKHL 2; [1932] All ER 494 at 499.
[15] [1932] UKHL 2; [1932] All ER 494 at 503-4.
[17] [1988] 15 NSWLR 130 at 136.
[18] [1994] VicRp 53; [1994] 2 VR 32.
[19] [1994] VicRp 53; [1994] 2 VR 32 at 67.
[22] [2005] VSCA 29 at [77]- [81].
[23] [1997] UKHL 19; [1997] AC 749.
[24] [1997] UKHL 19; [1997] AC 749 at 770-1.
[25] [2004] HCA 35; (2004) 218 CLR 451 at [22].
[26] [2004] HCA 52; (2004) 219 CLR 165 at [40].
[27] (1992) 27 NSWLR 326 at 332-3.
[28] It follows that, even if the second limb of cl. 7(b) were held to be void for uncertainty, the ESA obligation contained in the first limb would survive. It is separate and severable from the second limb, is unambiguous and has work to do even if the second limb of cl. 7(b) is not enforceable.
[29] Trawl Industries of Australia Pty Ltd v Effem Foods Pty Ltd (1992) 27 NSWLR 326 at 333, per Kirby P.
[30] I note that it was submitted on behalf of Mobil that, if the second limb of cl. 7(b) of the lease was void for uncertainty then the first limb should be struck down also. I have rejected this submission above.
[31] Reference was also made by Mr Mirkov to the New Zealand Oil Industry Guidelines issued in June 1999.
[32] Supreme Court (General Civil Procedure Rules) 1996 (Vic).
[33] I have already commented on the failure of Mobil to call Mr Amato, who was the author of the ESA, to give evidence. Nor did Mobil call the geologist or driller, who supervised and performed the field testing, to give evidence.
[34] As appears in the factual narrative, Mr Bond estimated that it would be prudent to remove at least 84 cubic metres of soil to remediate this hotspot.
[35] [1848] EngR 135; (1848) 1 Ex 850 at 855.
[36] Commonwealth v Amann Aviation Pty Ltd [1991] HCA 54; (1991) 174 CLR 64 at 80.
[37] Commonwealth v Amann Aviation Pty Ltd [1991] HCA 54; (1991) 174 CLR 64 at 104.
[38] [1994] HCA 4; (1994) 179 CLR 332.
[39] [1991] HCA 54; (1991) 174 CLR 64.
[40] [1991] HCA 54; (1991) 174 CLR 64 at 104.
[41] [1994] HCA 4; (1994) 179 CLR 332 at 355.
[42] [1994] HCA 4; (1994) 179 CLR 332 at 364.
[43] Commonwealth v Amann Aviation Pty Ltd [1991] HCA 54; (1991) 174 CLR 64 at 104.
[44] See Supreme Court Act 1986 (Vic) s. 58.
[45] The "Environmental Laws" are defined in the draft lease annexed to the proposed agreement for lease as "all laws and regulations, environmental protection policies, and directions, standards and guidelines of any authority (and any other like bodies) regulating or otherwise relating to the environment..."
[46] 22 May 2001 letter from Mr West to Mr Dugdale.
[47] 6 July 2001 e-mail from Mr Dugdale to Mr West.
[48] 20 July 2001 e-mail from Mr Dugdale to Mr West.
[49] Mr Samardjiev gave an uninformed estimate, but said he did not know how much new tanks would cost.
[50] $22,500 is 9 per cent of $250,000.
[51] Commonwealth v Amann Aviation [1991] HCA 54; (1991) 174 CLR 64 at 136; Bence Graphics International Ltd v Fasson UK Ltd [1998] QB 87 at 100.
Masha Nominees Pty Ltd
Mobil Oil Australia Pty Ltd [2006] VSC 15
(1994) 179 CLR 332
(1991) 174 CLR 64
(1968) 118 CLR 429
(2003) 215 CLR 317
(1982) 149 CLR 337
(2004) 218 CLR 451
(2004) 219 CLR 165
(1992) 27 NSWLR 326