Davis v Gosford City Council

The site and its locality 5The site is described as Lot 9 in DP787857. It is located in the north-western part of the SIP with an area of 11.097 ha although the proposed development occupies only an area of 4.05 ha. The site is vacant and largely covered by native vegetation of varying density. 6The western boundary of the site adjoins eight smaller industrial lots that front Somersby Falls Road. These lots contain a variety of industrial uses including warehousing, manufacturing, assembly, and a manager's residence. Access to the site is via an access handle between Lots 6 and 7. The site is 1 km south of the Australian Reptile Park.

Background to the appeal 7In December 2005 the applicant lodged a development application for a waste recycling facility on the site. A Species Impact Statement (SIS) prepared by Andrews Neil Pty Ltd accompanied the application. This application was refused by Gosford City Council in 2006 and was subsequently the subject of an appeal to the Court in 2007 [Davis v Gosford City Council [2007] NSWLEC 795] (the 2007 appeal). The appeal was heard and dismissed by the former Senior Commissioner Roseth. 8In July 2011, the applicant lodged a new development application and accompanying Environmental Impact Statement (EIS). Council rejected the application on the basis that a SIS was required and was not provided. The applicant lodged a s 82B application for a review of this decision. This review was heard by council's Independent Development and Environment Panel where the council's decision to refuse the application was confirmed. 9In September 2011 the applicant filed Class 4 proceedings in the Land and Environment Court [Davis v Gosford City Council [2012] NSWLEC 62] where Lloyd J declared, amongst other things, that on the evidence before him at the time, an SIS was not required. 10In December 2011 the applicant filed the Class 1 application currently before the Court, the proceedings having been being adjourned pending the determination of the Class 4 matter.

The planning framework 11The site is zoned 4(a1) Industrial (General) under Gosford Local Environmental Plan 22 (GLEP 22) as amended by Gosford Local Environmental Plan 457 (GLEP 457). Industry is a use that is permissible with consent. The land surrounding the site is a mixture of 4(a1) Industrial (General) and 1(a) Rural (Agriculture). The latter is zoned under IDO No 122 and generally contains dwelling houses, rural activities and poultry sheds. 12Division 4 was included in GLEP 22 by GLEP 457 and applies to land at SIP. The relevant clauses are: 24 Aims of Division This Division aims: (a) to maximise the opportunity for industrial development in the Industrial Park so as to provide employment opportunities in the Gosford local government area, and (b) to protect ecologically significant land and land with Aboriginal heritage characteristics within the Industrial Park (as identified as Management Zones 1 and 2 in POM Somersby Industrial Park (2005), as prepared for the Council), and (c) to ensure that the function and appearance of future subdivision or other development of the Industrial Park: (i) is of a high standard (in terms of both the built form and landscaping), and (ii) protects ecologically significant land and land with Aboriginal heritage characteristics within the Industrial Park, and (d) to provide that subdivision of land occurs in a flexible manner to take account of ecologically significant land and land with Aboriginal heritage characteristics within the Industrial Park, and (e) to ensure that development on land within Zone No 3 (a2) (Business) is of comparable bulk and scale to industrial development within the Industrial Park, and (f) to facilitate the provision of retail or commercial services to support the workforce of the Industrial Park in a single, central location so as to enable the full range of the workforce's needs to be met efficiently. 25 Development applications In determining a development application relating to land to which this Division applies, the consent authority must have regard to: (a) Plan of Management Somersby Industrial Park (2005), as prepared for the Council, and (b) the aims of this Division (as referred to in clause 24). 13The Plan of Management Somersby Industrial Park (2005) (POM) applies. The site (excluding the access handle) is shown on Figure 3.1 as being partly affected by "Combined Significant Habitat" and partly affected by "Aboriginal Management Zone". The northern part of the site is designated "Habitat Corridors and Linkages". Figure 4.1 and 4.3 (See Attachment 1) identify the following management zones within the site:

• Management Zone 1(a) - Aboriginal Heritage Sites,
• Management Zone 1(d) - Hibbertia procumbens Habitat,
• Management Zone 1(e) - Riparian and Habitat Protection Zone
• Management Zone No 2 - Habitat Links, and
• Road closure. 14The effect of the proposed development on the zones and sub-zones is summarised in the following table. Management Zone/ Sub-zone Description Location on site Proposed incursion Zone 1: Aboriginal heritage South-eastern corner No Sub-zone 1(a) Zone 1: Hibbertia procumbens Central northern portion Yes - by 1.4ha Sub-zone 1(d) Zone 1: Riparian zones and habitat protection North-eastern boundary No Sub-zone 1(e) Zone 2 Habitat links Northern boundary No

15The only management zone in dispute is Hibbertia procumbens Habitat Management Zone although the remainder of the south-western corner of the site, not affected by any management zones (the developable area), was subject to disagreement over the impact on the Eastern Pygmy-possum. 16The relevant parts of the POM are Section 1.1 - Overview that contains the following outline of the reasons for the development of the POM. The SIP is a significant economic and environmental resource in the Central Coast area. Over time, items of ecological and indigenous heritage value have been identified in the Park, including threatened flora and fauna species, and Aboriginal sites and artefacts. These items have caused a high level of uncertainty as to the intensity and location of development that can take place within the area, as well as generating concern over potential delays in assessment of development applications. The satisfactory resolution of these matters is a key project outcome. 17Section 1.3 Objectives of the POM states: The POM brings together in a single document the central findings of various investigations in the SIP that will facilitate assessment of development and management of the SIP. The POM will allow more effective management of the SIP through conservation and protection of significant values of the area. The objectives of the POM as stated in the study brief are to: 1. Identify areas where development can proceed (subject to development assessment and approval processes). 2. Identify areas of biodiversity value that should be protected. 3. Identify sites of Aboriginal heritage significance, as well as areas of significance to the Darkinjung people. 4. Identify management strategies for the future protection and conservation of the SIP, including mitigation and monitoring works required. 18Connell Wagner on behalf of Gosford City Council prepared the POM. In 2003, Connell Wagner undertook a number of ecological studies across the SIP. In 2005, Connell Wagner was commissioned to undertake additional investigations to determine the distribution of Hibbertia procumbens as it was considered that a prolonged drought during the earlier survey period might have restricted its occurrence. Prior to the Connell Wagner studies, the Australian Museum Business Services prepared a Species Assessment Report for the SIP in 1997 19As we understand from the evidence, it was expected that the POM would lead to a new LEP and DCP for the SIP however the reference to the POM was ultimately incorporated into GLEP 22 by way of GLEP 457. Nonetheless, cl 25 of GLEP 22 requires "that in determination of a development application the consent authority must have regard to the Plan of Management Somersby Industrial Park (2005) (cl 25(a)) and the aims of Division 4 (cl 25(b)).

Is the application an abuse of process? 20Mr Fraser, for the council, submits that the proposal warrants refusal as there is no material difference between the current application and the 2007 application refused by the Court. He relies on the decision in Russo v Kogarah Municipal Council (1999) 105 LGERA 290 at 292 [9] whether it states: The current application, being more or less precisely the same application as the first and second, both of which were appealed and dismissed by the Court, is an abuse of process of the Land and Environment Court, and ought not be permitted to proceed.... 21Mr Fraser submits that the changes between the current application and 2007 application are relatively minor with the only notable changes being the intrusion into the Hibbertia procumbens management zone, the compliance with the Aboriginal management zone boundary and the extension of the northern boundary of the development by some 2500 sq m. 22Mr Pickles, for the applicant, disagrees. He submits that any submission to strike out proceedings that have been fully heard is futile and should have been made prior to the hearing commencing. In any event, the question of whether proceedings are an abuse of process of process is, in all likelihood, a question of law. Mr Pickles further submits that decision in Russo involved exceptional circumstances compared to the current application and 2007 application. These are set out in detail in Mr Pickles submissions together with other reasons why this contention should be rejected. 23Having considered the detailed written submissions provided by the parties, we find it unnecessary to address the submissions beyond stating that we are satisfied that the 2007 application is not "more or less precisely the same application" as the current application. In our opinion, the differences between the two applications identified by Mr Fraser are sufficient to reject the suggestion that the current application is an abuse of process. The differences between the two applications clearly raises the need for a different assessment to that carried out for the 2007 application even though the application is principally for the same use. By way of example, the current application involves new evidence on the Eastern Pygmy-possum that was not available when the 2007 application was considered. This evidence ultimately results in a different approach to the issue of the Eastern Pygmy-possum found on the site.

The statutory framework 24The Eastern Pygmy-possum is listed in Schedule 2 of the Threatened Species Conservation Act 1995 as Vulnerable. Section 10(4) states: (4) A species is eligible to be listed as a "vulnerable species" if, in the opinion of the Scientific Committee: (a) it is facing a high risk of extinction in New South Wales in the medium-term future, as determined in accordance with criteria prescribed by the regulations, and (b) it is not eligible to be listed as an endangered or critically endangered species. 25The NSW Scientific Committee - Final Determination for the Eastern Pygmy-possum states: 1. The Eastern Pygmy-possum Cercartetus nanus (Desmarest, 1818) is a small arboreal marsupial that is distributed in the south-eastern corner of mainland Australia and in Tasmania. In New South Wales the species is found in coastal areas and at higher elevation in the south, but north of Newcastle at higher elevation only. Pygmy-Possums are agile climbers that feed mostly on the pollen and nectar from banksias, eucalypts and understorey plants and will also eat insects, seeds and fruit. 2. Although the Eastern Pygmy-possum is broadly distributed, recent studies have shown that within this range the species appears to be patchily distributed and its overall abundance is low. 3. Despite a large number of intensive trapping programs undertaken in the eastern forests and woodlands of New South Wales in recent years, only a small number of captures (154) have resulted from a total trapping effort of 315,000 Elliott trap-nights and 57,000 pitfall trap-nights (Bowen and Goldingay 2000). 4. Other detection techniques such as spotlighting, predator scat analysis, hair tubes and trapping in trees have produced similar low rates of detection. Capture rates are highest for installed nest-boxes and traps set in flowering banksias. This may reflect a habitat preference or a more successful trapping method. 5. From these and more recent studies (A. Tulloch, pers. comm.) there were only six, localities where more than 10 observations of Pygmy-Possums have been made. These were the Pilliga area, New England Tablelands, Barren Grounds Nature Reserve-Budderoo National Park, Royal and Heathcote National Parks, Kioloa State Forest and the Eden area. 6. The factors threatening the survival of the Eastern Pygmy-possum include isolated sub-populations with little opportunity for dispersal which increases the risk of local extinction, clearing that results in habitat loss and fragmentation, inappropriate fire regimes that remove nectar-producing understorey plants, the loss of nest sites due to past intensive forestry and firewood collection, and predation by foxes and cats. 7. In view of 2, 3, 4, 5 and 6 above, the Scientific Committee is of the opinion that the Eastern Pygmy-possum Cercartetus nanus is likely to become endangered unless the circumstances and factors threatening its survival or evolutionary development cease to operate, and is therefore eligible for listing as a vulnerable species.

The evidence 26Much of the discussion between the ecological experts, Mr Fanning for the applicant and Ms Ashby for the council, focused on the impact of the proposal on the local population of the Eastern Pygmy-possum and the efficacy of the relocation/ habitat enhancement measures proposed by Mr Fanning. The ecologists agree that the Eastern Pygmy-possum has been recorded in the southern parts of the proposed development site, and in bushland nearby, with the greatest numbers to date (9) being recently recorded in the area proposed to be cleared for the proposed development in the developable land. Another three individuals were found in one shelter tube in an area closely adjoining the developable land. They also agree that nearby areas support plant species that may provide the range of foraging resources required by the Eastern Pygmy-possum, however, the quality of those resources was in dispute. 27While Mr Fanning states that there will be an adverse impact on the local population of the Eastern Pygmy-possum and that the loss of habitat in that area will be irreversible, he considers that the proposed development will not place the local population at risk of extinction. In his 2011 'Flora and Fauna Assessment Report' (Appendix 3 to the EIS that accompanied the development application), Mr Fanning states that while the proposal "would involve the removal of the best quality habitat currently present on the subject site for the Eastern Pygmy Possum, as well as other potential habitat for this species, there will be a substantial area of potential habitat for the Eastern Pygmy Possum retained both on the subject site and in the vicinity following development as proposed." The area of Banksia to be removed is described elsewhere in that report as being 'prime habitat for the Eastern Pygmy Possum'. Elsewhere in his report Mr Fanning notes that 'Eastern Pygmy Possum populations are sedentary, and radio tracking studies indicate that movements are generally small". 28Mr Fanning's position is that considerable suitable habitat will remain in areas contiguous with the development site and that the loss of habitat for the Eastern Pygmy -possum from the developable area will not significantly affect the survival of the Eastern Pygmy-possum population in the general location. 29The amelioration and mitigation measures proposed by Mr Fanning include a trapping program, supplementary planting of Banksia ericifolia on the eastern part of the site, carrying out clearing works outside of the winter season when foraging resources are more constrained, and possible supplementation of food resources during the winter period. While Mr Fanning accepts that a trapping program would be unlikely to capture all individuals, it is preferable to no trapping at all. 30Ms Ashby states that the area consistently shown by surveys to support the Eastern Pygmy-possum is located in or near the mature Banksia thicket in the developable area of the site, despite there being other areas nearby with a similar suite of plants. In her view, apart from being a winter food source, the dense structure of the Banksia thicket provides protection from predators as well as horizontal connectivity within the canopy. That part of the site also provides a variety of habitat, high numbers of nectar producing plants, and a high incidence of insects to supplement their diet in harder times. She considers that while the surrounding area contains some or all of these features, it is younger (probably as a result of the 2005 fire) and may be less suitable for foraging or shelter. 31Ms Ashby considers that given the number of findings of the species, over time and in the same general area, this is a resident breeding population and the largest recorded population on the Central Coast. In her opinion, the removal of almost the entire Banksia thicket will make extinction of the local population of Eastern Pygmy-possum highly likely. 32In response to Mr Fanning's proposed amelioration measures, Ms Ashby states (with support, in part, by references to the scientific literature) that to her knowledge, trapping and relocation has not been attempted. Given the lack of understanding on the species as well as the lack of knowledge of the demographics of the population in question and any adjoining populations of Eastern Pygmy-possum, relocation could have unacceptable consequences such as skewing the population by capturing some individuals and not others (eg. juveniles or females with young in the pouch), placing stress upon the animals as they become familiar with a new site (as well as exposing them to more risk of predation), possible territorial behaviour, and potential competition for food resources thus stressing many individuals. 33In response to replanting and food supplements, Ms Ashby argues that replacement planting could take 15 years to provide similar features for foraging and shelter, the adjoining bushland is in good condition and does not need enhancing, and that the only study she is aware of in regards to supplementary feeding was limited and found no overall effect on the abundance of the Eastern Pygmy-possum.

The submissions 34Mr Pickles submits that unlike Mr Fanning, Ms Ashby did not undertake a formal assessment of significance pursuant to s 5A of the EPA Act and therefore her opinion on the risks to the local population should be given less weight. He further submits that strict adherence to the identified developable area in the POM would see the loss of the entire core Eastern Pygmy-possum habitat and that the proposal protects all of the Riparian - Habitat Protection Management zone, a zone designated in the POM to provide habitat and connectivity for a range of species including the Eastern Pygmy-possum. 35Mr Pickles considers that if the Court finds that there is likely to be an unacceptable impact on the Eastern Pygmy-possum (given the 'ground-truthing' by trapping conducted by Ms Ashby) then similar ground-truthing of the distribution of Hibbertia procumbens would suggest a balanced outcome could be achieved by the shifting of the development site further into the Hibbertia procumbens management zone in order to retain as much of the Banksia thicket (and consequent Eastern Pygmy-possum habitat) as possible. He submits that this, in addition with other mitigation measures proposed by Mr Fanning, would significantly reduce any impact on the Eastern Pygmy-possum. 36Mr Fraser accepts that had the applicant applied for a development in the area not affected by any management zones, then approval could have been granted. Similarly, given the new findings on the extent of the Eastern Pygmy-possum on the site, the council accepts that there is direct conflict between the POM and the Eastern Pygmy-possum. 37He submits that even though Ms Ashby did not undertake a s 5A assessment of significant impact, the evidence suggests that when considering s 79C(1)(b) there will likely be an unacceptable impact on the Eastern Pygmy-possum and on this basis, the appeal should be dismissed.

Findings - Eastern pygmy-possum 38We were taken to the south-western corner of the site and the location of the proposed resource recovery activity. This area contains a dense stand or thicket of mature Banksia ericifolia assumed by the ecologists to have escaped the 2005 fire. We were shown a number of tubes designed to provide shelter for the Eastern Pygmy-possum. Ms Ashby's tubes were of cardboard construction and Mr Fanning's were made from PVC pipes. It was in this general area that Ms Ashby found up to 12 individual Pygmy-possums sheltering in the tubes. 39We accept that with the benefit of the site inspection, the expert evidence and considering s 79C(1)(b) of the EPA Act as to "the likely impacts of that development, including environmental impacts on..the natural..environment(s)....in the locality" ,we are satisfied that the impact of the proposal on the Eastern Pygmy-possum is unacceptable for a number of reasons. 40First, and while we acknowledge that the habitat area for the Eastern Pygmy-possum is within an area of the site that is not affected by a management zone in the SIP, this does not in any way preclude the consideration required by s 79C(1)(b) of the EPA Act. 41Second, the basis on which the management zones, including the background studies, were created needs to be fully understood. After reading the 2003 Connell Wagner Flora and Fauna Report, it is unsurprising that the area on the site set aside for development was determined. Neither the Australian Museum Business Services' survey in 1997 nor the 2003 surveys conducted by Connell Wagner found any Eastern Pygmy-possums. Based on potential habitat, Figure 8.2(e) the 2003 Connell Wagner Flora and Fauna Report maps the Eastern Pygmy-possum habitat within the site but to the eastern portion of the applicant's lot (rather than the south-western part of the site where the prime Banksia thicket habitat is located). We note that the south-western part of the site is where the majority of the Eastern Pygmy-possums were subsequently found. 42We accept that, for the reasons stated in the 2003 Connell Wagner Flora and Fauna Report, including the difficulty of trapping the animals, the nature of the traps (Elliot traps), the relatively limited extent of the surveys, and the fact that the surveys were conducted before the 2005 fire, the management zones in the POM were determined on the best information available at the time but ultimately were not particularly accurate. 43Third, the most recent surveys support Ms Ashby's evidence there is a resident breeding population, most likely located in or near the prime Banksia thicket in the area of the proposed development. Appendix D of the 2005 Andrews Neal Species Impact Statement includes the s 5A assessment of the Eastern Pygmy-possum. This states that four individuals were found on the applicant's land. Two individuals were captured and another found in a nest box in the Banksia thicket on the southern part of the development site. The remains of another individual were found some distance away in a fox scat. In addition two individuals of this species were also caught by Andrews Neil ecologists on an adjacent property immediately to the south of the subject site in 2004. 44These survey results needs to be compared to the recent survey work undertaken by Ms Ashby where she installed 100 specially designed passive tube traps throughout the southern section of the proposed development site and the full extent of the Habitat link zone to the north and throughout the Riparian/Habitat zone and Aboriginal heritage zones on the eastern portion of the site. She states that the density of the traps was the same for all areas. 45What cannot be disputed is that Ms Ashby found up to nine individuals within the proposed development site with another three found sharing a single tube within about 20 m to the east of the proposed development site. She relevantly states that "the disproportionately high numbers in the development area reflect a deliberate choice for the development area by the animals rather than a reflection of sampling bias." 46The evidence from the parties' ecologists confirms the Scientific Committee's finding #4 in that the Eastern Pygmy-possum is difficult to detect. However, the evidence from Ms Ashby's 'tubes' is that up to nine individuals have been found in the area proposed to be cleared for the development, with another three found close by. While it is not known if these were separate individuals, this appears to be a significant new finding given the Scientific Committee's finding #5. 47Fourth, we are not satisfied that the question in s 5A(1) of the EPA Act as to "whether there is likely to be a significant effect on threatened species, populations or ecological communities, or their habitats" has been satisfactorily addressed. The earlier comments on the Eastern Pygmy-possum in the 1997 Australian Museum Business Services' survey and the 2003 Connell Wagner Flora and Fauna Report, the 2005 Andrews Neal Species Impact Statement have been overtaken by the most recent survey results from Ms Ashby. While we accept that Lloyd J in Davis v Gosford City Council [2012] NSWLEC 62 found, on the evidence before him, that an SIS was not required, this conclusion also pre-dates Ms Ashby's survey results. 48Mr Fanning reviewed these and other ecological studies in the preparation of the 2011 Flora and Fauna Assessment report that accompanied the EIS. He also established 20 nest boxes specifically designed to be attractive to the Eastern Pygmy-possum, however, no individuals were found. Based on this information and the existence of suitable habitat elsewhere, we understand how Mr Fanning arrived at his conclusion that the proposed development would not have a significant impact on the local population of Eastern Pygmy-possum. 49While we accept that Ms Ashby was not required undertake an assessment in accordance with s 5A of the Act, we are satisfied that her oral evidence and the substance of her report legitimately raise the question of whether there is likely to be a significant effect on a threatened species, population, ecological community or their habitats. 50Fifth, in regards to Mr Fanning's proposed amelioration measures, we prefer Ms Ashby's evidence as it appears to be supported by the relatively limited scientific literature on the species. In essence, there is a high degree of uncertainty regarding the habits of the species in general, and the demographics of the local population, in particular. We accept that while trapping and relocation appears attractive, it may have unintended and detrimental consequences. We also agree that the opportunities for enhancement of the nearby vegetation are limited. 51Sixth, we do not accept the suggestion that we should take a flexible approach to the application of the POM in regards to the Hibbertia management zone to compensate for the retention of at least part of the Banksia thicket on the southern part of the site that has been set aside for development. While we accept that the designation of management/ development zones in the POM was based on the best information available at the time, we also accept that the underlying reason for the preparation of the POM was to try and achieve a balance between areas where development can proceed (cl 1.3.1 of the POM) and areas of biodiversity value that should be protected (cl 1.3.2 of the POM). The proper balance, in our view, needs greater consideration that can be given as part of the assessment of a single development application. Clearly, a more considered strategic approach is required if any adjustment of the existing management zones is to be contemplated. 52For these reasons, we find that the proposal, pursuant to s 79C(1)(b) of the EPA Act, will likely unacceptably impact on the Eastern Pygmy-possum in the locality. We also find that the proposal is inconsistent with cl 24(b) in that the proposal does not "protect ecologically significant land" 53In our view, the likely impact on the Eastern Pygmy-possum warrants the refusal of the application.

The statutory framework 54Hibbertia procumbens is listed in Schedule 1 of the TSC Act as Endangered. Section 10(3) states: (3) A species is eligible to be listed as an "endangered species" if, in the opinion of the Scientific Committee: (a) it is facing a very high risk of extinction in New South Wales in the near future, as determined in accordance with criteria prescribed by the regulations, and (b) it is not eligible to be listed as a critically endangered species. 55The council modified its position on the incursion into the Hibbertia procumbens Habitat Management Zone by accepting that the proposed incursion would be acceptable if the applicant provided a suitable offset area. The applicant advised that no offset was required and none was offered. We understood the council to maintain some objection to the encroachment into the Hibbertia procumbens Habitat Management Zone as this zone is likely to be used as corridor for fauna.

The evidence 56The site and the proposed development area were inspected and Mr Fanning and Ms Ashby identified Individual specimens of Hibbertia procumbens. The area of incursion into the Hibbertia procumbens Habitat Management Zone was identified and this area was observed to have less vegetation cover than nearby areas and showed signs of disturbance. Possible reasons were advanced for the disturbance, that included the effects of a fire in late 2005, an unknown disease or some other unknown disturbance. 57The topics discussed by the ecologists focused largely on the applicability of biodiversity certification methodology used by Ms Ashby given the concession by the council that the encroachment into the Hibbertia procumbens Habitat Management Zone was acceptable if an appropriate offset was provided. On the matter of Ms Ashby's biodiversity certification methodology, some time was spent discussing the appropriateness of the methodology. In the joint report Ms Ashby relevantly states at [6.1 a.5]: When the SIP PoM was developed, there was no quantitative assessment procedure to measure the efficacy of the environmental outcome. The relatively new Biodiversity Certification procedure now provides a qualitative tool and I applied it in this matter in order to understand whether the PoM can withstand further losses to its inherent conservation framework. 58Ms Ashby also maintained that the management zones were created as 'offsets' (although the term was not in use at the time) to protect biodiversity and other significant features. In her opinion, if biocertification methodology had been used, the area set aside for biodiversity protection across the whole of the SIP would be inadequate. She considers that if the current biobanking requirements were applied, the loss of natural vegetation from the development site, including the incursion into the Hibbertia procumbens Habitat Management Zone would require a significant area of land to be provided as an offset. 59Ms Ashby's survey was largely confined to the part of the Hibbertia management zone proposed for the development. She considers the numbers to be significantly less than suggested by Mr Fanning. In her opinion, the distribution of plants across the site is patchy creating several separate populations. If the proposed development is approved, this will result in the loss of approximately half of one of those populations as well as the loss of potential habitat. Along with edge effects and the threat of fire, Ms Ashby considers the proposal could place the local population at risk of extinction. 60Ms Ashby considers that the current relative scarcity of the Hibbertia procumbens in the Hibbertia procumbens Habitat Management Zone may be partly due to a fire in late 2005 or to other factors such as an unknown disease or some other disturbance. In her view, when Connell Wagner undertook their survey work that led to the mapping of the management zones, there were probably more plants on the site. 61In Mr Fanning's opinion, biodiversity certification has no relevance to the development application as this is something applied for by a planning authority (s 126J Threatened Species Conservation Act 1995 (TSC Act)). Nor has there been an application for a Biobanking Statement pursuant to s 7A of the TSC Act. In Mr Fanning's opinion, based on the number of surveys he conducted both inside and beyond the Hibbertia procumbens Habitat Management Zone, there are thousands of plants comprising the 'local population', with most being outside the Hibbertia procumbens Habitat Management Zone. In his view the proposed incursion into this management zone will have an insignificant impact on the local population.

Submissions 62Mr Fraser submits that given the extent of the Hibbertia procumbens across the site, the proposed incursion into the Hibbertia procumbens Habitat Management Zone would not be a reason for refusal of the development as long as the applicant provided a suitable offset. Apart from the loss of Hibbertia procumbens, Mr Fraser argues that the Hibbertia procumbens Habitat Management Zone is also important because of its use by other species and therefore an offset would have wider benefits. He contends that this is supported by maps in the Connell Wagner report that show the area would be used by other threatened species such as the Adams Emerald Dragonfly, Heath Monitor, Eastern Pygmy-possum as well as forest birds, amphibians and flying mammals. 63Mr Pickles submits that as the land is zoned for industrial use, it should be assumed that an industrial use should be permitted. He submits that aims (a) and (b) in cl 24 GLEP 22 are conflicting in their purpose - that is maximising opportunities for industrial development while protecting ecologically and culturally significant land. While regard must be had to the POM, he argues that compliance with the management objectives contained within it is not mandatory. He submits that given the evidence that Hibbertia procumbens was more prolific outside the Hibbertia procumbens Habitat Management Zone, the impact of the proposed development on it would be moderate at most. 64In regards to the council's requirement for an offset, Mr Pickles submits that there is no requirement in GLEP 22 or the POM that mandates this and no more should be expected of the applicant as 65 % of the site has already been set aside for conservation purposes.

Findings 65As we understand it, biocertification and the concept of biobanking post-date the ecological studies carried out for the preparation of the POM. In our view, the POM is essentially self sufficient in that the POM attempts to strike a balance by setting aside areas for protection and at the same time allowing other areas to be developed. While we understand the rationale behind Ms Ashby's use of the biocertification methodology, we agree with the applicant that it is not a matter that is necessarily relevant to these proceedings. If an offset was offered by the applicant for the encroachment into the Hibbertia procumbens Habitat Management Zone then that is a matter that could be considered. There is no requirement in the POM or GLEP 22 for the provision of an offset for the encroachment into any management zone. With no offer of an offset, the relevant question to be answered is whether the encroachment into the Hibbertia procumbens Habitat Management Zone is likely to have an unacceptable impact on the Hibbertia procumbens in the locality, pursuant to s 79C(1)(b) of the EPA Act. 66In response to this question, the experts agree that the plant is not confined to the Hibbertia procumbens Habitat Management Zone. With the benefit of the site view and the guidance from the experts, we observed the distribution of Hibbertia procumbens across the site - both inside and outside the area proposed to be developed. We agree that the proposed incursion into the Hibbertia procumbens Habitat Management Zone would have a moderate impact on the distribution of Hibbertia procumbens and in itself, would not be a reason for refusal of the development given the degraded nature of the area sought for the encroachment into the Hibbertia procumbens Habitat Management Zone and the strong likelihood that other plants are located outside the Hibbertia procumbens Habitat Management Zone in other management zones on the site and surrounding properties (see Figure 1: Hibbertia procumbens Habitat, Supplement Report, Somersby Industrial Flora/Fauna Report). 67On the question of whether the Hibbertia procumbens Habitat Management Zone should be retained in full, to provide a corridor for fauna, we are satisfied that the principal purpose of the zone is to protect the Hibbertia procumbens and while the area may provide secondary functions, such as a fauna corridor, the test of whether it may be removed rests largely on the impact on its principal function of protecting the Hibbertia procumbens. We note that areas that serve as a wildlife corridor are specifically designated for this purpose. For example, the most northern part of the site is specifically designated Management Zone No 2 - Habitat Links.

Orders 68The orders of the Court are:

1. The appeal is dismissed.
2. Development Application No. 40918/2011 for a waste resource recovery facility at 168 Somersby Falls Road, Somersby is refused.
3. The exhibits are returned.

G T Brown Commissioner of the Court

J. Fakes Commissioner of the Court DISCLAIMER - Every effort has been made to comply with suppression orders or statutory provisions prohibiting publication that may apply to this judgment or decision. The onus remains on any person using material in the judgment or decision to ensure that the intended use of that material does not breach any such order or provision. Further enquiries may be directed to the Registry of the Court or Tribunal in which it was generated. Decision last updated: 30 November 2012