Brookwood Land Pty Ltd v Shoalhaven City Council

Brookwood Land Pty Ltd v Shoalhaven City Council - [2025] NSWLEC 1019 - NSWLEC 2024 case summary — Zoe

Background

SF9821 was originally lodged in 2006. At the time of consideration of the original application, the Threatened Species Conservation Act 1995 was in play in regard to development which may have a significant effect on threatened species, populations or ecological communities or their habitats. It so happens that subsequently, there have been substantial amendments to the statutory framework for the assessment of biodiversity impact of development applications by the introduction of the Biodiversity Conservation Act 2016 and repeal of certain provisions of the EPA Act. I accept the agreed advice of the parties (filed 21 October 2024) that as the DA was made before those statutory changes came into effect on 25 August 2017, the DA is to be assessed under the former provisions.
In this case, a species impact statement (SIS) was prepared by the applicant which took account of the "Director-General's requirements" (DGRs), dated 16 August 2010, concerning the form and content of the SIS (DGRs were documented at p 287 of the SIS at Tab 8 of the Class 1 Application filed on 15 March 2023 (Ex D)). Among other things, the DGRs indicated that the ameliorative measures described for this development "should meet the improve or maintain test for biodiversity values" (Ex D Tab 8 p 298).
The DA, including the finalised SIS (accommodating revisions in response to requests for further information), was referred to the Office of Environment and Heritage (OEH) for concurrence under then s 79B of the EPA Act (because of its potential to "significantly affect a threatened species, population, or an endangered ecological community or its habitat").
On 10 May 2013, the OEH issued a report and conditions of concurrence, having regard to a third party review. The concurrence report included the following commentary (Ex D Tab 9 pp 4-5). "… The modified proposal … will involve the clearing or disturbance of a total of approximately 25 hectares of relatively undisturbed native vegetation, which is known or potential habitat for threatened species. Approximately 13 hectares will be removed or disturbed in stage 1 and 12 hectares in Stage 2. On the basis of OEH's assessment of all relevant information, OEH concludes that whilst the modified proposal … will not have a significant impact on local populations of the Eastern Pygmy-possum or the Powerful Owl, there will still be impacts to threatened species including the Glossy Black-Cockatoo, Yellow-bellied Glider and threatened microbats from loss of hollow-bearing trees and foraging habitat. These impacts can be reduced through adherence to tree retention conditions in the [Environmental Management Plan] for residential lots. In particular, retention of trees referred to as medium and high habitat class in Figure 22 of the SIS prepared by OMVI within the residential lots will maintain a proportion of viable habitat for these and other species."
The OEH concurrence was conscious of the particulars of Council's proposed conditions of consent, as per a "draft determination" (Ex D Tab 9 p 3): "… Specific conditions of consent were recommended in Councils' Draft Determination with regard to retention of key threatened species habitats, the creation of an in-perpetuity conservation lot, and the provision of an environment management plan (EMP), conservation management plan (CMP - which applies to the conservation lot) drainage plan, landscaping plan, habitat retention plan, and tree removal plan. For OEH to provide concurrence to this approval, it is imperative that all of these conditions are met by the proponent."
Because of their essential pertinence to the proceedings, the OEH concurrence conditions, which were incorporated into the initial consent, need to be reproduced in full and were as follows: "Condition 1: An in-perpetuity Conservation Area (referred to in this document previously as the Conservation Lot) must be created. 1.1. The creation of a Conservation Area, as recommended in the Shoalhaven City Council's Draft Determination (Figure 1). Condition 63(0) of Council's consent makes clear that this Conservation Area is to be managed in perpetuity, for the purpose of conservation of threatened species habitat. No development is to occur within this Reserve. 1.2. The management of the Conservation Area is to be funded by the proponent in accordance with a Conservation Management Plan (CMP). 1.3. The Conservation Management Plan is to be approved by the Office of Environment and Heritage (OEH) prior to the issue of a Construction Certificate for Stage 1. Condition 2: ln-perpetuity protection of Conservation Area must be legally secured 2.1 An appropriate legal mechanism to guarantee the management of the conservation lot in perpetuity must be applied, through registration on title. 2.2 This registration on title should only be able to removed or varied with the consent of the Minister for the Environment. 2.3 To satisfy Condition 2.1 and 2.2, the following options could be considered: a) A covenant or user restriction under s88 of the Conveyancing Act 1919 that is separate to the covenant or user restriction applying to the whole of the site (including Stage 1A and Stage 2). This separate covenant or user restriction applying solely to the Conservation Area would be required to be in favour of Shoalhaven City Council w the Minister for the Environment (or delegate). The proponent and any future owners shall comply with all relevant restrictions on the use of the land imposed under this user restriction, where the Office of Environment and Heritage is the authority empowered to vary those restrictions, in consultation with Shoalhaven City Council. b) and / or with the agreement of the proponent, a Conservation Agreement under the National Parks and Wildlife Act 1974 a Trust Agreement under the Nature Conservation Trust Act 2001, or a Bio-banking Agreement under the Threatened Species Conservation Act 1995. Condition 3: Re-wording of Conditions 5 (1) and 5 (2) in Shoalhaven City Council's Draft Determination Report 3.1 Condition 5 (1) should be reworded to: 1) Tree/vegetation retention plan clearly identifying all areas/ vegetation to be retained (in particular hollow bearing trees) - pre construction identification & works and maintenance works. This plan shall be prepared by a suitable qualified ecologist detailing the following: a) Vegetation to be retained including identification of specified habitat trees including: i all hollow bearing trees identified in the SIS prepared by Omvi as of medium or high habitat tree class as indicated in Figure 22 of the SIS. Where possible, all hollow bearing trees identified as low habitat tree class should also be retained. ii Where possible all Allocasuarina Iittoralis trees should be retained, particularly those trees indicating evidence of recent (last 12 months) Glossy Black Cockatoo feeding activity iii All trees located within the road reserve, except those trees to be removed for road construction and other services and safety reasons iv All structurally stable trees not required to be removed to fulfil asset protection zone requirements or to accommodate building envelopes and driveways or the provision of services. b) A tree protection plan for those trees that are to be retained must be prepared by a suitably qualified and experienced [arborist] in accordance with AS 49700-2009 Protection of trees on development sites. The trees that are to be retained are to be protected during all works strictly in accordance with the tree protection plan. c) Each tree to be retained shall be identified by a number, its species, number and size of hollows and health 3.2 Condition 5 (2) should be reworded to: (2) Tree/Vegetation removal plan for vegetation in the residential lot area including road reserves and is to be prepared by a suitably qualified ecologist detailing the following, All other wording in clause 5 (2) should remain as per the draft determination."
Consequently, SF9821 was partly determined by Council on 16 May 2013. Condition 1 of the 2013 consent notice stated (Council's bundle of documents, Ex 3 p 160): "This consent relates to a proposed residential subdivision including 30 residential lots, one 'conservation' lot with building area, 1 public reserve and road reserves, and 1 'development lot' for further subdivision…".
The approved plans referenced in Condition 1 (in particular Ex 3 pp 190, 578) identified the initial 30 residential lots and identified a conservation lot (with a dwelling entitlement).
Condition 3 of the 2013 consent identified the residue land as being subject to a revised design and future supporting documentation. It was referred to as the "development lot": "This is a staged consent granted under section 80(4) of the Environmental Planning Act as follows. Stage 1 - comprised of the [30 residential lots] …. Stage 2 - the "development lot" or the "in-principle area is the first stage of the development consent for subdivision of the subject land. It is to be the subject of a future submission that provides a revised design and documentation that specifically addresses as a minimum the following: i) Re-design of lots, roads, services, drainage and bushfire mitigation measures to accommodate provision of the conservation lot as per attachment 1; … ix) Tree retention."
There have been two modification applications approved in relation to the 2013 consent. On 14 February 2014 the consent was modified, among other things, to increase the number of residential lots within the first operational stage (Ex 3 p 755B).
On 10 March 2015, the consent was further modified. The provisions of Condition 8, relating to the submission and approval of a conservation management plan (CMP), were amended, in particular, the provisions of Condition 8(l) were amended to state: "The works as outlined in the Conservation Management Plan, shall at cost to the applicant, be undertaken in accordance with the schedule of works (Appendix G). Documentary evidence of compliance with relevant works outlined in the schedule of works shall be submitted with the subdivision certificate for each stage".
Perhaps of some relevance is that Appendix G of the approved CMP dated December 2014 (Ex 3 p 752) indicated the cost of carrying out the various ongoing management works relating to habitat maintenance and enhancement as (essentially) $39,750 per year.

[5]

Evidence in regard to potential threatened species habitat impacts

The OEH concurrence conditions and the accompanying commentary provides important evidence, in my opinion. It seems clear that there has been considerable deliberation in regard to potential impacts of development on the land occupied by the proposal before me based on the SIS (as revised), the third party review and Council's own evaluative material. There is a finding that rural residential subdivision of the site would not have a significant impact on local populations of the Eastern Pygmy-possum or the Powerful Owl. The concern is that there would "still be impacts to threatened species including the Glossy Black-Cockatoo, Yellow-bellied Glider and threatened microbats from loss of hollow-bearing trees and foraging habitat" (see [6]). A strategy to "reduce" these impacts was determined and can be understood to be documented in the concurrence conditions (if not already referenced in consent conditions by way of OEH reference to Council's draft determination).
The interpretation of the wording of the consent conditions is a matter that I need to consider in detail when addressing the applicant's arguments. But suffice to say here that Mr Coddington argued that the concurrence conditions required the retention of all of the medium and high value HBTs on the site as a requirement of any subdivision consent. To not do so would bring about "an unacceptable adverse impact on the natural environment, particularly threatened species habitat" (Ex 11 par 9).
Mr Ryan highlighted the changes over time to the proposal concerned with minimising loss of medium and high value HBTs. He also thought it critical, when considering biodiversity impacts, to consider the "whole context of the subdivision and the overall environmental outcome" and the "mitigation and amelioration measures already in place". A series of factors were listed including in relation to conservation of Powerful Owl and Eastern Pygmy Possum habitat, fencing, weed and pest management, biodiversity monitoring since 2014 (Ex 11 par 23). Mr Ryan also highlighted the scale of the area of land associated with the conservation lot (some 20.9 hectares (ha) in area, some 43% of the original parcel) (Ex 11 par 22) and management efforts to date to conserve and rehabilitate it.
I can note here a little imprecision in my understanding of how many medium and high value HBTs would actually be lost with the proposal. At this point, I can also introduce the naming system in regard to the staging of the overall development which was adopted by the parties in the proceedings (which was clear but differed a little in regard to the naming system adopted over time). Essentially, as I understand the naming system adopted by the parties, "Stage 1" comprises the subdivision which became operational with Council's 2013 consent, including the subsequent modifications. "Stage 2" and "Stage 3" concern the subdivision before me, here: Stage 2 comprises the more western area and Stage 3 the more eastern area. They are separated by the conservation lot.
In regard to the medium and high value HBTs which would be lost with the proposal before me, finally in these proceedings, firstly I note Council's Contention 2(h) (Ex 1 p 9) indicated that the applicant's then tree retention plan shows the removal of 27 medium and high value HBTs across Stages 2 and 3; sourcing OMVI's Biodiversity Update Report of May 2024 (Ex G Tab 4 final two pages). I note that the applicant indicated a prospective loss of 26 medium and high value HBTs (Applicant's Outline of Submission (AOS) par 11 and Tcpt, 26 September 2024, p 170(27)). However, I think that this number may not take account of the supplementary expert ecology report (Ex 11), which found that with certain amendments to the proposal and the re-evaluation of certain of the HBTs associated with the August 2024 plans, the net equivalent of a further six medium and high value HBTs would be retained. I have assumed that something in the order of 20 medium and high value HBTs would be lost with the proposal now before me.

[7]

Proper interpretation of concurrence conditions would not require retention of all medium and high value HBTs

According to the applicant, concurrence conditions "only required the EMP to show how such tree retention would occur during the pre-construction, identification and maintenance phase of the development … (there) was no requirement to show in the EMP all HBT's to be retained in the residential lots and the road reserves" (AOS par 7). Council argues that the OEH concurrence conditions require retention of medium and high value HBTs in the residential blocks.
While there were (necessary) references to the condition numbering system associated with the consent for Stage 1 in the proceedings (2013 consent), when considering this application for the grant of a further development consent (applying to Stages 2 and 3), it is both practical and appropriate for me to refer directly to the OEH concurrence documentation cited at [6]-[10].
Firstly, I turn to the text itself, which should be at the centre of this question of interpretation. The relevant wording is part of the OEH's "Condition 3". Condition 3 is, I note, concerned with the redrafting of conditions in Council's draft determination, but the text is discrete in its terms (in the sense of having a capacity to be understood alone). Condition 3.1 (as reproduced at [8]) is concerned with the preparation of a tree/vegetation retention plan which shows the trees (among other things) to be retained. Condition 3.1a), concerned with the detailing of the tree/vegetation retention plan, is explicit in its indication that vegetation, to be retained, includes medium or high habitat trees as identified in Figure 22 of the SIS. I reproduce this figure below. Figure 1 Hollow bearing tree (HBT) species and scores (source: Figure 22 in SIS as reproduced in ROS par 9)
The applicant's submissions, as I understand them, are that chapeau provisions at Condition 3.1, and thus affecting the operation of Condition 3.1a) place limitations on which of the medium or high habitat trees as identified in Figure 22 of the SIS would need to be captured in the tree/vegetation retention plan under Condition 3.1a), and thus would need to be retained.
Firstly, I note that the applicant is inexact in its description of the phrase (which I recognise is predicated by a hyphen) at the centre of interpretive focus. The phrasing referenced by the applicant in some of its submissions is "pre-construction, identification and maintenance phase of the development" (eg AOS par 7). Rather, the applicable phrasing is "pre construction identification & works and maintenance works" (reproduced at [8]).
While I accept that the interpretation of the phrasing " - pre construction identification & works and maintenance works"; is not without difficulty, the explanation I think most likely is that this phrasing is attempting to indicate that the tree/vegetation retention plan is concerned with identifying trees and vegetation to be retained across the development's phases (ie (1) "pre construction" preparation efforts, (2) the physical development "works", and (3) post works "maintenance").
The works phase can be considered to include both the development engineering works and the housing works, I note that such works have indeed been attempted to be identified in versions of the tree retention plans before the Court (with the identification of potential building areas, on-site effluent management areas and the like). I also recognise, I think, the parties agreed position that subdivision consent conditions do not, of themselves, bind a future development application for, say, housing development on one of the lots created: Hillpalm Pty Ltd v Heaven's Door Pty Ltd (2004) 220 CLR 472; [2004] HCA 59 at [43].
The explanation for reference in Subcondition 3.1a)(iii) of the concurrence conditions (reproduced at [8]) to "(all) trees located within the road reserve, except those trees to be removed for road construction and other services and safety reasons"; opens the door to removal of medium and high value HBTs required to be removed for road construction.
While I think the text is readily interpretable (as indicated above), if I step behind the text to the concurrence report, there is nothing there that persuades me other than the conclusion I draw above. The consideration of threatened species issues is documented in the concurrence report. There is documented interest, in the retention, "in particular", of medium and high habitat trees within the residential lots. This is as a means of "(maintaining) a proportion of viable habitat" for threatened species including the Glossy Black-Cockatoo, Yellow-bellied Glider and threatened microbats (refer second half of quotation at [6]). That is to say, while there would be still an impact associated with other habitat loss, retention of the medium and high value HBTs would maintain a proportion of viable habitat. There is a clear line of sight between this interest of OEH (documented in the concurrence report) and the text in the concurrence conditions indicating that the vegetation to be retained (and identified in the tree/vegetation retention plan) includes: "(i) all hollow bearing trees identified in the SIS prepared by Omvi as of medium or high habitat tree class as indicated in Figure 22 of the SIS…"
The interest in retaining low habitat trees "where possible" is also identified.
The applicant's interpretation of the condition does not provide an adequate response to the OEH clear interest in retention of medium and high HBTs in residential lots, as documented in the report accompanying the concurrence conditions.
In all of the circumstances, I am more convinced of Council's interpretation of the OEH concurrence conditions with respect to retention of medium and high value HBTs.

[8]

Even if concurrence conditions required retention of all medium and high value HBTs, this was never expected or possible

The applicant drew attention to Stage 1 where, notwithstanding the OEH concurrence provisions, numerous medium and high value HBTs had been removed during the works stage, including with Council approval of individual house plans. For example, attention was drawn to "clusters of HBTs located within approved residential lots making it unlikely that a house can be constructed without removal of HBTs" (AOS par 10).
Generally, there are significantly fewer high and medium HBTs indicated for the Stage 1 development, when compared with Stages 2 and 3, and certainly the conservation lot (readily evident from Figure 22 to the SIS and reproduced at Figure 1 above). But I do note the Figure 22 drawings indication of a cluster of high and medium HBTs at the north-western sector of the Stage 1 development. I can agree with the applicant that one of these parcels (at the north-eastern corner of this north-western sector) would have particular difficulty in locating a house pad. However, that is not to say this would be impossible, with responsively sensitive design.
I do not think these submissions of the applicant have convinced me other than the concurrence conditions should be taken at face value. On this point, I see the applicant as looking for an interpretation at odds with the text of the condition, itself. In terms of, perhaps, applicable background, OEH makes clear that it has undertaken a disciplined analysis prior to establishing its concurrence provisions and drawn conclusions on how land development within this site should respond to threatened species habitat concerns. Certain of the habitat can be lost but high and medium HBTs need to be retained (unless they are related to the road construction). I do not see decisions of Council, or another certifying authority, for housing-related development, relating to Stage 1 as being useful in my interpretation of the intentions of the original concurrence conditions.

[9]

OEH had indicated a willingness to reconsider recurrence conditions in acknowledgement of implementation difficulties

The applicant referred to OEH correspondence suggested to indicate a willingness on the part of OEH (or now described as the Biodiversity and Conservation Division of the Department of Planning and Environment, henceforth BCD) to reconsider the concurrence conditions (dated 11 March 2021 and 7 April 2022 (Ex 3 pp 1333-1334 and pp 1335-1336, respectively)). This indication of flexibility was argued to be in acknowledgement of the difficulty of implementation of those conditions, including in association with the changes to either habitat values or condition of specific trees since the SIS was prepared in 2013. The applicant also argued that since this correspondence there had been further changes which provided for retention of some further medium to high value HBTs, concerning which there has been no feedback from BCD.
Having reviewed this correspondence, I did not see BCD as departing from the original concurrence conditions, per se. This was made clear for example in the correspondence dated 7 April 2022, were BCD indicated: "It is important the proponent assists the process by 'demonstrating that impacts to biodiversity are not inconsistent with the original concurrence'".
The standout aspect of the correspondence referred to by the applicant and the small bundle of correspondence added to Ex 3 (Tcpt, 26 September 2024, p 113 (44)), related to a suggested BSA. A letter from BCD had indicated prospects for a formal amendment to the concurrence conditions, albeit while seeking to "(ensure) the best conservation outcomes for the site" and involving a BSA (Ex 3 p 134). A letter from Southbank Land Pty Ltd & Huntingdale Developments Pty Ltd dated 31 March 2022, suggested that such a pathway was some little way advanced (seventh and eighth pages of the small bundle of correspondence attached to Ex 3). A letter from M Saxon of BCD (undated, but linked to an email dated 18 May 2022) also infers a BSA may be in-train.
I think I understand the applicant to here be arguing that there was an OEH/BCD recognition of the applicant's difficulties, in retaining all of the medium and high value HBTs, while securing, essentially, the subdivision yield it sought to achieve. The applicant's argument might suggest this recognition of difficulty would sway the Court to the view that today, including with the most recent amendments, BCD or its equivalent would be satisfied with the loss of in the vicinity of 20 additional medium and high value HBTs. I reject this line of argument. My interpretation of the correspondence is that a BSA was a fundamental factor in any substantive softening of the position requiring compliance with the original concurrence conditions. The BCD's linking of a (conservation lot-related) BSA to this consideration of habitat loss in Stages 2 and 3 was not in my view unreasonable given the evidence of improved biodiversity outcomes overall falling from the more rigorous conservation management system associated with BSAs.

[12]

When considering the zoning of the site and the positive outcome associated with the conservation lot, together, the proposal warrants conditional consent

I interpreted the applicant to be arguing three major points here. The first was that if the concurrence conditions were enforced this was tantamount to a refusal of the balance of the proposed development. There was no evidence provided to support this argument. For example, it was not shown that it was impossible or impractical to redesign the proposed subdivision as Mr Coddington suggested in evidence was necessary to achieve compliance with the concurrence conditions. This would decrease the number of future lots.
The second point was that the Court should take a practical approach to the prospective likelihood that HBTs will be removed on future lots (with the detailed house block designs) and that "such an outcome will achieve the overall balance sought by the Department in its concurrence" (AOS par 14). My understanding is that OEH/BCD were not happy with the result of the Stage 1 development and the loss of additional medium and high value HBTs. On the material before me what OEH/BCD and Council is seeking to achieve with the detailed schemas for housing lots (house pads, effluent management areas, area protection zones and a consciousness of gradients), is the actual retention of the medium and high value HBTs. The fact that "practicalities" prevented this occurring with Stage 1 should not predicate Stages 2 and 3. Setting aside any BSA, what Council and OEH/BCD would be satisfied with, it seems to me, is a subdivision and development layout which can practically deliver on the retention of the medium and high value HBTs which has been sought from the original consent. Were there to have been an assumption (eg on the part of OEH or Council) that many more of the medium and high value HBTs were to be lost in the housing development, the OEH concurrence provisions (or determination) may have been different.
The third point raised by the applicant to support the view that the zoning of the site and the positive outcome associated with the conservation lot, together, should make for a positive outcome goes to the question of balancing different evaluative factors. This seems to me to be the hub of the decision before me. I will deal with it in the next section.

[13]

Whether, on balance, the zoning and provision of a conservation lot, justifies the grant of consent

Ecological or indeed threatened species habitat concerns are not the only evaluative factor in development application assessment. I believe, the applicant is asking me to give considerable weight to the site's Zone No 2 (a3) Residential A3 zone under Shoalhaven Local Environmental Plan 1985 (SLEP). The single objective of the Residential A3 zone is as follows (Ex 3 p 3): "The objectives are to provide for a low density residential environment with a minimum allotment size of 4000 square metres primarily for detached housing."
The fact of the intended conservation lot (currently maintained by the applicant and), its management subject to an approved conservation management plan, also warrants considerable weight, according to the applicant.
These two considerations, for me, are supportive factors in relation to the proposal which need to be balanced against negative impacts, essentially centred on the implications of the loss of threatened species habitat (in this case for Glossy Black-Cockatoo, Yellow-bellied Glider and threatened microbats (see OEH commentary at [6]).
While this proposal does not compare in terms of its complexity with the project at hand in those proceedings, the evaluative process was usefully outlined by Preston CJ in Bulga Milbrodale Progress Association Inc v Minister for Planning and Infrastructure and Warkworth Mining Limited (2013) 194 LGERA 347; [2013] NSWLEC 48 (eg at [31]), where it was indicated that: "The exercise of the power … to approve or disapprove the carrying out of the Project requires consideration, weighting and balancing of the environmental, social and economic impacts of the Project. The range of interests affected, the complexity of the issues and the interdependence of the issues, means that decision-making involves a polycentric problem…."
In this instance, I can acknowledge the applicant's argument that it has done enough in regard to threatened species concerns and, with a mind to one aspect of the polycentric problem, perhaps related to the zone objective directly, the subdivision should be able to be completed, lots sold and housing built to accommodate families and others in an environment consistent with the zone objectives.
When I turn to the threatened species habitat loss aspect of the problem before me, my impression is that there has been a measured and informed analysis of impacts undertaken by then OEH which was reflected in the original concurrence conditions. There has never been any doubt of the requirement to provide for the conservation lot as part of the overall project (eg see concurrence Conditions 1 and 2 at [8]). There has then been a holding fast to the adopted conditions since by BDC, as far as I can tell from the material before me. I do note BCD's foray into the territory of a BSA to seek a way for a win-win outcome. This seems entirely understandable, if it is the overall biodiversity outcome that is of concern, given acknowledged difficulties with management of legacy conservation lots, without the rigour of the BSA approach. More generally, it is clear that the proposal does not provide for a maintain or improve outcome in regard to habitat for threatened species including the Glossy Black-Cockatoo, Yellow-bellied Glider and threatened microbats.
The Council's position, in my interpretation, essentially reflects this considered position adopted by OEH/BDC. It might also be said that this position of OEH/BDC is mindful of the evaluative work of Council.
I do acknowledge there has been some redesign of the proposal already which involved loss of a residential lot. However, the statutory scheme applying to the assessment of this application gives considerable weight to threatened species habitat protection, by way of the assignment of concurrence provisions in this instance. I do not see why the provision of the now proposed number of rural residential lots, still at or reasonably near the 4000m2 lot size minimum, outweighs the loss of medium and high HBTs, important to threatened species habitat, which would occur as a consequence of the proposed subdivision. The essence of the zone objective is to provide for "a low density residential environment", the reference to 4000m2 refers to a minimum and there is nothing to suggest all lots in a subdivision need to be near that mark. I think Mr Coddington is correct in his indication that greater design changes, albeit resulting in a significantly reduced lot yield, is necessary in this instance, to reasonably provide for high and medium value HBT retention (Ex 11 par 3). While I am mindful of BGP Properties findings in regard to weight to zoning (see [48]), in this case the current design of the project results in unacceptable environmental impacts.
I am also not persuaded by the applicant's argument that the determination of the particular application before me should be influenced by a hypothetical concern about the ultimate delivery of the conservation lot as a distinct parcel of land (AOS par 13). Condition 1 of the concurrence provisions, applying to the Stage 1 development, makes clear the requirement for its creation.
It is my opinion that the application before the Court, including having regard to consent conditions proposed by the applicant, does not warrant the grant of consent.

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Judgment (17 paragraphs)

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Cases Cited (7)