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[2003] NSWLEC 190
Land and Environment Court (NSW)
1992-08-05
Pain J, Bannon J, Talbot J, Stein J, Ms J
Original judgment source is linked above.
Introduction 1. The Defendant is charged by summons filed 21 January 2003 with one offence of causing waters to be polluted contrary to s 120(2) of the Protection of the Environment Operations Act 1997 (the PEO Act) on 23 January 2002 in the Oberon Council area in the State of New South Wales. At the time of the offence s 120(2) of the PEO Act provided "A person must not cause any waters to be polluted" . I note that s 120 of the PEO Act was amended on 1 July 2002 by the Environmental Protection Legislation Amendment Act 2002 so that the offence of pollution of waters is now contained in s 120(1).
Facts 5. There was a Statement of Agreed Facts provided by the parties which sets out the circumstances concerning the offence on 23 January 2002. Paragraphs 5.1 - 5.17 are as follows: 5.1 In January 2002 MAINSCLEAN had a contract with Trazlbat Pty Ltd to disinfect (super-chlorinate) new water mains in the Oberon Shire area downstream of Oberon Dam. MAINSCLEAN was to chlorinate the water mains to 50ppm with a detention time of 24 hours or to 100ppm with a detention time of 3 hours. 5.2 On 23 January 2002 the feed water for the 450mm main to be disinfected (main 2) came from an existing parallel main (main 1) that was connected to main 2 by a 50mm hose …
5.3 This was the first time that the defendant and the second time Mr Innes [an employee of MAINSCLEAN] had dealt with a bypass fed water main.
5.4 The flow in main 2 was not monitored by a flow meter at the first scour point on main 2 ("scour valve 1"). Scour valve 1 was approximately 300 metres from the injection point and down a steep slope from that point. Scour valve 1 was about 3 metres from an unnamed watercourse that flowed for about 50 meters before flowing into the Fish River.
5.5 Around 8am on 23 January 2002 Mr Innes was at the injection point and the defendant was at scour valve 1. Mr Innes connected the dosing equipment including the dosing pump and at about 8.15am he started the dosing pump to inject sodium hypochlorite into main 2. He notified the defendant by two-way radio when he had turned on the dosing pump. Using the MAINSCLEAN dosing charts it was estimated that it would take 52 minutes for the water containing the face of chlorinated water to arrive at scour valve 1.
5.6 Sometime after the dosing pump was connected to the main and prior to the pump being switched on, and/or whilst the pump was dosing, 180 litres of a 200 litre drum of sodium hypochlorite syphoned into main 2. Main 2 was overdosed during this period to about double the required strength of chlorine.
5.7 Approximately 32,000 litres of chlorinated water passed through scour valve 1 and into the unnamed watercourse and then into the Fish River. The chlorinated water exited scour valve 1 from a blue pipe that protruded from the ground near a large manhole.
5.8 Around 8.45am Mr Innes rang the defendant by two-way radio and told him he had a problem and asked him to close the scour which was done.
5.9 Mr Innes then replaced the empty drum of sodium hypochlorite with a new drum of sodium hypochlorite which he commenced injecting into the main and he contacted the defendant by two-way radio to tell him pumping had restarted and to open scour valve 1 again. When informed of this the defendant tested the level of total chlorine at scour valve 1 and states it was then 100ppm so he immediately closed the scour.
5.10 Mr Innes states that within a few hours of the injecting of sodium hypochlorite into the main above scour valve 1, and around lunch that day, he walked down to the Fish River and saw a few dead fish in the river.
5.11 From 8.45am to 6.15pm the defendant and Mr Innes continued disinfecting other sections of main 2. [This included operations at scour valve 7/8]
5.12 At approximately 6.15pm the defendant saw dead fish in the Fish River. He and Mr Innes together inspected about a 200 metre stretch of the river downstream of scour valve 1 and the defendant saw approximately 10 dead fish in that part of the river.
5.13 The defendant supervised the disinfecting process on 23 January 2002.
5.14 At 7.26pm the defendant telephoned by mobile phone Oberon Council's Director Engineering Leigh Robins to advise them of the fish kill. At 7.46pm the defendant telephoned by mobile phone Oberon Council's Development and Planning Manager Kenneth Solman. Mr Solman spoke with the defendant. The defendant informed Mr Solman, "we have had a chlorinated water discharge into the Fish River … ". Mr Solman arranged to meet the defendant at the site and advised him to notify the Environment Protection Authority ("EPA").
5.15 The defendant phoned the EPA pollution line at 7.55pm to report an incident.
5.16 About 8.30pm Mr Solman inspected part of the Fish River downstream of scour valve 1 with the defendant and Mr Innes. Mr Solman saw four dead fish in the river. He ceased his investigation of the river as it became dark.
5.17 Mr Solman decided that the Fish River should be flushed with water from Oberon Dam and he and the defendant met with Mr Martin Duffy of the Fish River Water Supply Authority at about 9pm to discuss this. Following that conversation water was released that night from the dam to dilute and disperse the chlorine in the river. 6. As the Defendant's counsel is arguing that s 10 of the Crimes (Sentencing Procedures) Act 1999 ought to apply it is important to consider all of the objective circumstances of the matter including the investigation of the offence on 24 and 25 January 2002 by the Prosecutor and the Defendant. The Defendant provided two reports to the Prosecutor about the incident, the first on 24 January 2002 and the second on 25 January 2002.
Between 8.15 am and 8.45 am Allan Innes had a problem with syphoning of sodium hypochlorite directly into the water main using 180 litres in half an hour. The usage should have been 43 litres per half hour. Clearly the main was overdosed to 209 ppm for this half hour period.
David Collis did not start testing for diluted sodium hypochlorite until after the slug of highly chlorinated water came through the scour from the syphoning event and down the unknown stream and then into the Fish River. Cause of the incident 9. The Statement of Agreed Facts states at par 8.1 that: The EPA engaged Mr Phineas Stone, an engineer and principal consultant specialising in hydraulics to provide his expert opinion about the incident. According to Mr Stone the most probable cause of the incident was that the dosing pump was connected but not started, scour valve 1 was opened and the flow in the main adjusted to the desired level, and while this occurred a pressure was induced in the pipeline at the sodium hypochlorite injection point that was lower than atmospheric pressure. The cause of the low pressure was the large difference in heights between the injection point and scour valve 1 together with the fact that water was being supplied at the top by a 50 mm hose rather than the 500 mm main pipe. The reduced pressure meant sodium hypochlorite would have been flowing (syphoning) into the main pipe before it was expected and without that fact being appreciated by the operators.
Environmental harm 10. The matters in relation to environmental harm are agreed. Paragraphs 10.3 and 10.4 of the Statement of Agreed Facts are as follows: The release of the chlorinated water from scour valve 1 on 23 January 2002 effectively "sterilised" at least 600 metres of the Fish River killing 60 trout. Additionally it is likely that other less visible aquatic life such as aquatic insects and plankton, were lethally affected.
This type of spill does not result in long term contamination of waterways. During the inspection of the site on 15 February 2002, by Mr Julli, several live trout were observed resident in the area of the 23 - 24 January 2002 fish kill, indicating that recruitment of fish from downstream sites had commenced. Similarly a range of aquatic invertebrates were also present in the affected section of the Fish River indicating recolonisation had commenced. Other evidence 11. The Prosecutor relied on the affidavits of Mark Clyne, an environment protection officer employed by the Prosecutor, sworn 15 November 2002, Moreno Julli, an environment protection officer employed by the Prosecutor, sworn 13 March 2003, and Phineas Stone, an engineer and principal consultant specialising in hydraulics and coastal engineering, sworn 12 March 2003.
Should s 10 of the Crimes (Sentencing Procedure) Act 1999 be applied? 15. Before considering the matters in relation to penalty under s 241 of the PEO Act it is appropriate to deal with the Defendant's submission that s 10 of the Crimes (Sentencing Procedure) Act 1999 ought to be applied.
Who owns MAINSCLEAN? 18. The statement of agreed facts states at [4.1] that: The Defendant is the manager of MAINSCLEAN which conducts pipe cleaning and disinfecting. The defendant has been the manager for 14 years. David Collis and Associates Pty Ltd is the trustee for the Collis Family Trust trading as MAINSCLEAN. David Collis is a director and a shareholder of David Collis & Associates Pty Ltd. 19. I note that there was evidence of these statements provided in a letter from an accountant (exhibit C, tab 14) and also in a letter from MAINSCLEAN to the Prosecutor and other material provided to the Prosecutor at the time a notice for information and records was issued by the Prosecutor to the Defendant and to David Collis & Associates Pty Ltd.
Defendant's submissions on s 10 21. The Defendant firstly submitted that as s 10 is applicable to environmental offences the Court should not dismiss applications made under these provisions because it considers that no environmental crime is "trivial".
No doubt some further guidance or training might have made a difference in each case, but it is difficult to identify any effective step which the master could have taken that does not require virtual perfection. 25. It was contended that the Defendant should be regarded as an employee and manager of MAINSCLEAN, as set out in the Statement of Agreed Facts, rather than the owner of the business. The Defendant's counsel argued the reasoning in Thorneloe should apply to the Defendant who, as an employee of MAINSCLEAN, could have done nothing to avoid the pollution incident from scour valve 1.
The Defendant's counsel's submissions also quoted extensively from the decision of Bignold J in Environment Protection Authority v Excel Fuels Pty Limited [2002] NSWLEC 160, particularly [41] - [53]. The defendant in that case conducted a fuel distributorship business. In relation to s 10(3)(b), the trivial nature of the offence, Bignold J took into account that the offence was serious because of the introduction into a stormwater drain and a creek of 400 litres of diesel fuel that were not recovered in cleanup operations. He also considered the defendant's subjective culpability was serious because of the absence of proper procedures and protocols for the operation of the oily water separator, and the absence of training for any employee at the depot in the operation of the separator as part of the infrastructure of a fuel storage and distributor operation which was inherently dangerous by the nature of the goods handled. The Defendant's counsel submitted this situation was to be contrasted with the Defendant, whose employer MAINSCLEAN had an operations manual which set down procedures to be followed and provided training to its employees.
In the circumstances of this case, the Defendant is an employee of MAINSCLEAN and, while in charge of operations on the day of the offence, was located out of sight of the operator of the dosing pump, Mr Innes. Only Mr Innes could have been aware of the amount of sodium hypochlorite which entered the mains water and he did not tell the Defendant of that circumstance. This, combined with the unusual operating environment, meant that there was nothing the Defendant could have done to avert the offence on 23 January 2002 as it had occurred by 8.45am. The objective circumstances of the incident show that by 8.45 am the chlorinated water had already discharged into the Fish River and environmental harm had occurred. Mr Collis was not in a position to have prevented this from occurring even if he had been told of the syphoning event at that time. It is the evidence of Mr Collis that he only became aware about 3.30 pm on 24 January 2002 that a spill had occurred and he initially believed it was from scour valve 7/8.
Considering matters in s 10(3)(a), a number of written references concerning the Defendant's character were provided to the Court which attest that he is careful and thorough in his work. He has no previous convictions for environmental offences. There was also a statement from a clinical psychologist attesting to the negative impact the prosecution has had on the Defendant.
In relation to s 10(3)(c), it was submitted that because the circumstances in which the offence was committed are unique and outside the usual frame of reference for the Defendant, the offence was committed in extenuating circumstances.
It was submitted that in light of the character of the Defendant and in light of all the material put before the Court in mitigation, namely, the legal costs payable by the Defendant, the low income of the Defendant, changes implemented by MAINSCLEAN to ensure future spills will not occur, the Defendant has been operating for 14 years with no environmental record, the environment was recovering three weeks after the event, there was nothing the Defendant could have done to prevent the incident and the Defendant began immediate testing when he thought there was a problem arising from the scour valve 7/8, the Defendant ought not be punished for the events which occurred between 8.15 am and 8.45 am on 23 January 2002. Accordingly, s 10(1) should be applied.
Prosecutor's submissions on s 10 31. The Prosecutor argued that an order under s 10 is not generally appropriate in relation to a breach of environmental laws, relying on Hunter Water Board v State Rail Authority of New South Wales [No 2] (1992) 75 LGRA 22 and Environment Protection Authority v Attard [2000] NSWCCA 242. The Prosecutor's submissions were based on the assumption that the Defendant was the owner of the business MAINSCLEAN (although that is not what is stated in the Statement of Agreed Facts) and also the person in charge of operations on the day of the offence (which is not disputed by the Defendant).
Finding on s 10 Clause 10(3)(b) 37. The offence is clearly not trivial but is the Defendant's culpability trivial? The Defendant's counsel emphasised that the Defendant should be regarded as an employee not an owner of MAINSCLEAN. R v Olbrich (1999) 199 CLR 270 was referred to as authority for the proposition that matters which are to be taken into account in the Defendant's favour must be proved on the balance of probabilities. The Prosecutor is required to prove all matters adverse to the interests of the Defendant beyond reasonable doubt.
The evidence relied on by the Prosecutor to prove that the Defendant is the owner of MAINSCLEAN, namely the Business Names Extract for MAINSCLEAN, does not prove that fact beyond reasonable doubt. The Defendant's formal legal relationship with the business of MAINSCLEAN is that of an employee on the evidence relied on by the Defendant and I accept this has been proved on the balance of probabilities.
Is the Defendant the operator/manager of the business? The evidence (at par 40 - 42) suggests that the Defendant is not an "arms length" employee but rather is the manager and operator of the business. He is involved in the overall conduct of the business of MAINSCLEAN and has been for some time. Further, there is no evidence adduced by the Defendant that there was anyone else apart from himself who could have been in charge of the overall operation. I consider his role in relation to the operation of the business means that he can be considered to have responsibility for the failure of the systems used by MAINSCLEAN on the day of the offence.
The Court of Appeal decision of Thorneloe must be closely considered to see if the same reasoning should be applied here. In my view the circumstances of this case have some important differences to those in Thorneloe . This case involved actual and serious, albeit not long term, environmental harm, and there was release of a large volume of chlorinated water, namely 32,000 litres. One of the factors determining whether s 10 ought apply in Thorneloe was that the offence was minor, unlike in this case.
The Defendant in this case is a manager and operator of MAINSCLEAN. His involvement in the events leading up to the offence is different to the ship's captain in Thorneloe . The Defendant, as an experienced manager, is liable if he applies the usual MAINSCLEAN operating procedures in unusual circumstances where his experience should tell him caution must be exercised and fails to implement adequate procedures and use appropriate equipment. I note that based on the measures I have found could have been implemented in relation to s 241(1)(b) below, there were measures that could have been implemented to avert the offence.
I do not consider the Defendant's culpability is trivial.
Clause 10(3)(c) - (extenuating circumstances) 48. The fact the Defendant is experienced in the business of pipe cleaning and had not encountered this particular operating environment before is relied on by the Defendant to suggest there was an extenuating circumstance in this case. The Defendant's experience also suggests that he should have been more aware of the need to take different precautions in an unusual operating environment given the highly toxic nature of the chemicals being used. I accept the Prosecutor's submission and the evidence of Mr Stone at par 13 and 14 above, so that given the Defendant's experience he should have been aware that the usual procedures may not be sufficient and that greater caution was warranted. The fact that one of the means implemented since the incident includes the purchase of a $300 see-through limited capacity tank and that training procedures now include the need to advise of any irregularity in process, suggest that relatively simple measures were available to assist in ensuring such an incident could not occur. I do not consider extenuating circumstances exist.
Clause (10)(3)(a) 49. I note that Mr Collis' character references are excellent and attest to his careful work habits.
Defendant's submissions 55. The Defendant also highlighted the procedures he has now implemented as set out at par 9.1 of the Statement of Agreed Facts. The Defendant's counsel argued the dosage pump operated with a similar effect to the use of a flow meter and still would have required Mr Innes to notify the Defendant of the problem, the difficulty was rather with the changed pressure in the pipes which caused the syphoning to occur. Furthermore, this was the first time the Defendant had come across this arrangement of pipes. The Defendant's counsel further argued that in the circumstances there was nothing that the Defendant could have done to prevent or mitigate the harm.
Finding 58. I have already set out my findings in relation to the Defendant's relationship to MAINSCLEAN in relation to my finding on s 10 at par 44. Clearly there were practical measures that could have been taken by the Defendant, as manager and operator of the business, to prevent, control abate or mitigate the harm as identified by the Prosecutor at par 53 above. I do not however, accept the Prosecutor's submissions that the incident should have been reported earlier. Section 241(1)(c) - the extent to which the person who committed the offence could reasonably have foreseen the harm caused or likely to be caused to the environment by the commission of the offence Prosecutor's submissions 59. The Prosecutor submitted the likely harm was clearly foreseeable. The Defendant was using a highly toxic chemical in close proximity to a waterway. Further, until the repeal of the Clean Waters Act 1970, the Defendant's company, David Collis & Associates Pty Ltd, held a pollution control licence under that Act. That licence contained a discharge limit for chlorine of 1 mg/L when cleaning mains and a discharge limit for chlorine of 3 mg/L when disinfecting mains. The Defendant had operated under that licence for approximately ten years and should have been aware of the harm associated with a discharge of this nature.
Defendant's submissions 60. The Defendant submitted that it was not reasonably foreseeable that a syphoning event would have occurred so that 180 litres of sodium hypochlorite would flow through a water main and be discharged into the environment without it being noticed by the operator of the dosing pump. This, it was argued, required the Defendant to operate at a level of "virtual perfection" as identified by Spigelman CJ in Thorneloe at 186. It is unreasonable for the Court to impose an unwarranted standard of behaviour because of this particular situation. The matters identified by Mr Stone as to what should have been done (see par 13, 14) are matters which are beyond the procedures set down in the MAINSCLEAN manual. Further, Mr Innes' actions were not foreseeable and the Defendant, while responsible for procedures on the day, could not completely control Mr Innes' actions.
Finding 62. I accept the Prosecutor's submissions that the harm caused or likely to be caused was foreseeable by this Defendant. The harm caused to the environment by inadequate procedures and equipment being in place when using a highly toxic chemical in close proximity to waterways is clearly foreseeable. Section 241(1)(d) the extent to which the person who committed the offence had control over the causes that gave rise to the offence Prosecutor's submissions 63. The Defendant was in charge of operations on the day of the incident, which is admitted, and had control over the causes that gave rise to the offence. He told Mr Innes, the operator injecting the sodium hypochlorite into the main, when to start and stop the pump and gave him any other instructions . Further, the Defendant was at the downstream end of the main and failed to close scour valve 1 allowing the escape of the 32,000 litres of chlorinated water.
Defendant's submissions 64. It was the employee Mr Innes who was at the dosing pump where the sodium hypochlorite was injected into the main. The events contained in the Statement of Agreed Facts show that the process at scour valve 1 started at 8.15 am. At 8.45 am the Defendant was informed there was a problem, but not the extent. By the time the Defendant was notified there was any problem at 3.30 pm on 24 January 2002 the chlorinated water had passed through the mains and discharged into the Fish River, that is, by 8.45 am the damage had been done.
Finding 67. I accept that the Defendant did have control over the causes giving rise to the offence. As manager and operator of the business, and supervisor on the day, he is clearly responsible for the lack of procedures in place which led to the offence being committed.
Other sentencing matters 68. Regard must be had to the culpability of the defendant and the individual circumstance which led to the commission of the offence.
Deterrence 70. The Prosecutor argued that the environment protection legislation includes the need for general deterrence in sentencing: see Axer per Badgery-Parker at 367. The Prosecutor submitted a substantial sentence is required in these circumstances by way of general deterrence to ensure that other operators in the industry realise that adequate steps must be taken to ensure water is not polluted when using highly toxic chemicals such as sodium hypochlorite in close proximity to waterways.
Aggravated circumstances? 73. The Prosecutor also argued there were aggravated circumstances of this offence because of: 1. the size and toxicity of the pollutant 32,000 litres of chlorinated water polluted the unnamed watercourse near scour valve 1 and the Fish River. Chlorine is highly toxic to aquatic life. The release from scour valve 1 was approximately 230,000 times higher than the Australian and New Zealand Guidelines for Fresh and Marine Water Quality 2000. There is a heavy obligation on those handling dangerous chemicals to do so with the utmost care: Axer at 367 (Badgery-Parker J).
Evenhandedness 75. The Court is required to have regard to other sentencing cases where the facts of other offences are of a similar nature: Camilleri's Stock Feeds at 701 - 702. The Prosecutor referred to three matters. Firstly, Environment Protection Authority v Orange City Council (Stein J, NSWLEC, 23 June 1995, unreported) in which the Defendant pleaded guilty and was fined $25,000 (the maximum fine for a corporation was $120,000). The offence involved a chlorine spill from the Orange Olympic Pool during a routine filling of the chlorine storage tanks. In Environment Protection Authority v Egan (Bannon J, NSWLEC, 5 August 1992, unreported) the defendant pleaded guilty to a breach of s 16(1) of the Clean Waters Act 1970 and was fined $8,000 (the maximum penalty was $60,000). The defendant was a cotton farmer who had installed a tail gate drainage mechanism on his farm which was faulty. The pesticide Endosulphan escaped into a nearby creek causing the death of a number of fish. Another matter of Environment Protection Authority v Harris (Talbot J, NSWLEC, 19 February 1993, unreported) was referred to in which the defendant was charged with breaching s 16(1) of the Clean Waters Act 1970 and pleaded guilty. He was fined $12,000, the maximum penalty being $60,000. He was the co-owner and manager of a property where cotton farming was conducted. The property had been sprayed with an insecticide Thiodan. As a result of rain there was a large buildup of stormwater in channels on the property which contained the insecticide Thiodan. The stormwater escaped into a nearby creek causing death to fish and other aquatic organisms.
Means of the Defendant to pay 76. Under s 6 of the Fines Act 1996, in the exercise of its discretion to fix the amount of any fine, the Court is required to consider such information regarding the means of the accused as is reasonably and practicably available for the Court's consideration and such other matters as, in the opinion of the Court, are relevant to the fixing of that amount. The Court was provided with copies of the tax returns for Mr Collis for 2001/2002 showing that in 2001 he had a taxable income of $6,880. In 2002 his taxable income was $20,345. His ability to pay a substantial fine is limited based on these records, which are the only financial matters placed before me. While this information does not provide a complete picture of all of the Defendant's assets and liabilities I do take the information into account in assessing penalty.
Mitigating factors 77. There are also a number of mitigating factors that should be taken into account to reduce any penalty. Firstly, the Defendant pleaded guilty at the earliest opportunity. A plea of guilty entitles the Defendant to a discount in penalty under s 22 of the Crimes (Sentencing Procedure) Act 1999 in the range of 10-25%: R v Thomson; R v Houlton [2000] NSWCA 309; R v Sharma (2002) 54 NSWLR 300. I consider the Defendant is entitled to the maximum discount envisaged under R v Thomson of 25%.
Costs 81. During the hearing the Defendant's counsel indicated he wished to raise the issue of the quantum of the Prosecutor's costs, namely that the Court should limit the quantum of the Prosecutor's costs payable by the Defendant on the basis that those costs are excessive. The Prosecutor indicated that if anything other than the usual costs order in Class 5 proceedings was proposed by the Court it would need the opportunity to make submissions. I indicated to the Defendant's counsel that it would be more appropriate that I make the usual order as to costs in Class 5 proceedings and that any issue of quantum be left to the costs assessor, if the matter could not be agreed by the parties.
Orders 83. The Court orders that: 1. The Defendant is convicted of the offence with which he is charged. 2. The Defendant is fined the sum of $5,000 to be paid to the Registrar of the Court within 28 days of today's date. 3. The Defendant must pay the Prosecutor's costs of the proceedings against him, as agreed or assessed. 4. The exhibits may be returned.
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Environment Protection Authority
Collis
CITATION : Environment Protection Authority v Collis [2003] NSWLEC 190 PROSECUTOR Environment Protection Authority PARTIES : DEFENDANT David Richard Collis FILE NUMBER(S) : 50004 of 2003 CORAM: Pain J KEY ISSUES: Prosecution :- water pollution - strict liability offence - plea of guilty - culpability of defendant - whether owner of business or employee - application of s 10 of the Crimes (Sentencing Procedure) Act 1999 refused - consideration of penalty - mitigating factors - means to pay Crimes (Sentencing Procedure) Act 1999 s 10 LEGISLATION CITED: Fines Act 1996 s 6 Protection of the Environment Operations Act 1997 s 120, s 241 Axer Pty Ltd v Environment Protection Authority (1993) 113 LGERA 357; Camilleri's Stock Feeds Pty Ltd v Environment Protection Authority (1993) 32 NSWLR 683; Environment Protection Authority v Attard [2000] NSWCCA 242; Environment Protection Authority v Egan (Bannon J, NSWLEC, 5 August 1992, unreported); Environment Protection Authority v Excel Fuels Pty Limited [2002] NSWLEC 160; Environment Protection Authority v Harris (Talbot J, NSWLEC, 19 February 1993, unreported); Environment Protection Authority v Orange City Council (Stein J, NSWLEC, 23 June 1995, unreported); Hunter Water Board v State Rail Authority of New South Wales [No 2] (1992) 75 LGRA 22; CASES CITED: Peter Carter v Verna Wall [2003] NSWLEC 94 ; R v Andrew [2002] NSWSC 489; R v Goh [2002] NSWCCA 234; R v Olbrich (1999) 199 CLR 270; R v Paris [2001] NSWCCA 83; R v Piccin (No 2) [2001] NSWCCA 323; R v Thomson; R v Houlton [2000] NSWCA 309; R v Sharma (2002) 54 NSWLR 300; Thorneloe v Filipowski (2001) 52 NSWLR 60 DATES OF HEARING: 02/06/2003 DATE OF JUDGMENT: 08/27/2003
(1993) 113 LGERA 357
(1993) 32 NSWLR 683
(1999) 199 CLR 270
(2002) 54 NSWLR 300
(2001) 52 NSWLR 60