13 At [87]-[88] of their judgment, the Commissioners stated:
87 As a consequence of all this development application and related material, we are of the view that a number of factual observations should be made. These are as follows:
With respect to all of the development consents relating to on-site disposal of effluent, there is no specific condition of consent that incorporates conditions relating to the composition of the waste whether solid or liquid;
With respect to all of the development consents relating to on-site disposal of effluent, there is no specific condition of consent that incorporates conditions relating to dilutions rates of whatever might be within the waste;
With respect to all of the development consents relating to on-site disposal of effluent, there is no specific condition of consent that incorporates conditions precluding on-site disposal of solid waste and such on-site disposal of solids is, in fact, specifically diagrammatically depicted in the flow chart appended to the 1992 Statement of Environmental Effects;
The document entitled Volumes Requiring Irrigation in appendix 2 to the Statement of Environmental Effects accompanying the 1992 development application does not propose any limit on the volume of liquid effluent to be disposed of but, if it were read to be proposing a limit, postulates that the volume of liquid effluent capable of being disposed of safely on the site under then average rainfall conditions would be 2.75 times the volume proposed to be permitted under the present application.
88 As a consequence of these factual observations and what we have earlier discussed concerning the present operation of the tannery's effluent disposal process (ignoring Mantons), we are of the view that a number of conclusions can be drawn. These are:
First, the disposal of waste, solid and liquid, other than discharge of effluent to the sewer (at its most restrictive for the applicant and expressing no view as to whether this restriction actually applies or not) is unregulated by any relevant condition of development consent except for requirements contained in:
o condition 2 of the 1983 consent concerning the amenity of the neighbourhood;
o condition 3 of the 1983 consent requiring compliance with Department of Industrial Relations and Technology conditions (if imposed);
o conditions 4 of the 1983 consent requiring a Clean Air Act licence and that any conditions of such a licence would form part of the consent;
o condition 2 of the 1992 consent requiring submission of quarterly review statements on the operation of the effluent treatment system; and
o condition 4 the 1992 consent requiring, in effect, a pollution reduction program acceptable to the EPA to be aimed at prevention of further degeneration of the irrigation area. EPA approval of this pollution reduction program was to be obtained prior to the release of the building application arising from this development consent.
Second, as a consequence of what is set out above, it is not possible to determine what would be the permitted environmental impacts of the existing or approved development except that the comparatively unrestricted nature of these conditions, to the extent that they might be valid, means that those environmental impacts are potentially significantly high as the degree of regulation and control provided by the conditions of development consent is very permissive.
Third, the absence of any certain relevant concentration, composition or volumetric restriction coupled with the limited present monitoring regime required by the EPA licence reinforces the second conclusion we have drawn above.
Fourth, if there is some volumetric restriction to be imputed from the 1992 development consent, this volumetric limit is at least 2.75 times the limit proposed to be conditioned for this application.
Fifth, the regime proposed by the conditions of consent as agreed to by the parties and as determined by us as discussed below is a significantly restrictive regime.
Sixth, the present effluent disposal activities of the applicant (ignoring Mantons) are unsatisfactory both in their impact on the surrounding community and their likely impact on the tannery's own land to the extent that this impact can be assumed given the unsatisfactory monitoring regime currently applying.
Finally, the regime proposed by the conditions to attach to a development consent arising from this application, although applying to different land areas to those subject of the presently approved effluent disposal activities of the applicant, is one that inevitably lead to a position where the development together with the additions or alterations will not only not significantly increase the environmental impacts of the total development that is presently approved but must, in our view, in fact, decrease the maximum potential environmental impacts necessarily inherent from the present approved development.
14 The Commissioners conclude at [89] that Walfertan has the benefit of the exception in cl 35 Sch 3 of the Regulation without the need to rely on any development consent or entitlement of the abattoir and that no EIS is required. I have set out the judgment in some detail as it is necessary in a s 56A appeal to ensure that the context for the Commissioners' decision making is clear. That generally requires a consideration of the judgment as a whole.
Evidence
15 The Second Respondents relied on parts of the transcript of the proceedings before the Commissioners. The extensive exhibits from those proceedings were also tendered. A number of these were referred to in the course of this appeal.
Walfertan's existing and proposed effluent disposal changes
16 Further detail about the proposed changes in the effluent disposal system ought be noted to enable an understanding of the issues in this appeal. As noted above at par 5, the proposal before the Commissioners is described broadly in the judgment at [11]. Paragraphs [31]-[45] describe the present effluent disposal practices of the tannery and the proposed changes to them.
17 Walfertan's counsel provided in oral submissions a detailed explanation of the existing and proposed procedural stages of effluent disposal by reference to exhibit 17 showing the geographical features and boundaries of the total site (TS 3 March 2010 p 167 line 34 - p 179 line 47). Development consent is sought to construct an irrigation pipe within the existing open channel between the wastewater treatment system on lot 53 DP 739487 and the 107ha area of lot 159 DP 712988 (the eastern irrigation area). The proposal includes use of substantial additional areas for irrigation and subsequent cropping, being lot 159 (blue area below the dam, exhibit 17) and part of lot 53 (grey area, exhibit 17). Irrigation of other areas known as Manton's and Salt Sacrifice used previously is to cease in whole or for certain waste disposal and these areas are to be rehabilitated; [36], [45] Walfertan No 2.
18 It is also useful to note that Walfertan's DA lodged with the Council originally sought to vary the development consent for the abattoir that once operated on the site. This DA was changed to one seeking consent for the use of lot 159 and lot 53 for effluent disposal/irrigation purposes.
Grounds of appeal
19 There was considerable discussion during the hearing over about five days about the grounds of appeal and these were amended more than once. In the Second Further Amended Summons Commencing an Appeal (the amended summons) filed in Court on the fourth day of hearing the Second Respondents submitted that:
1. The Commissioners:
(a) Erred in failing to hold that the application was for designated development; and/or
(b) Should have held that the application was for designated development.
2. The Commissioners erred in incorrectly applying cl 35 of Sch 3 of the Environmental Planning and Assessment Regulation 2000 ("the EP&A Regulation"), in the following ways:
(a) The Commissioners erred in construing and wrongly applied the following consents:
DA 64/83 granted 21 December 1983 (the 1983 Consent);
DA 57/89 granted 20 November 1989 (the 1989 Consent);
DA 57/90 granted 15 October 1990 (the 1990 Consent); and
DA 26/92 granted 18 May 1992 (the 1992 Consent);
and thus failed to identify the "existing or approved development" and its impacts. (see Error 1)
(b) The Commissioners failed to apply ss 106, 107 and 109(2) of the Environmental Planning and Assessment Act 1979 and make the comparison required by cl 35 of Sch 3 of the EP&A Regulation on the basis that either:
(i) There was no "existing or approved development", or
(ii) Alternatively, if there was "existing or approved development" that that development was not unlimited,
and thus failed to take into account relevant matters. (see Error 2)
(c) In applying cl 35 of the EP&A Regulation, the Commissioners took into account irrelevant matters; namely the impacts of present activities which were not impacts of the lawfully existing or approved development; (see Error 2)
(d) Having found that it was "not possible to determine what would be the permitted environmental impacts of the existing or approved development" (at [88]) the Commissioners erred in finding that they was satisfied of the matters in cl 35 in the absence of evidence enabling the comparison required by cl 35 to be made. (see Error 3)
(e) The process of reasoning of the Commissioners in holding that they were satisfied of the matters in cl 35 in the absence of evidence enabling the comparison required by cl 35 to be made was irrational. (see Error 4)
3. … (This ground is not pressed)
4. The Commissioners failed to give reasons for concluding that there was an "absence of any certain relevant concentration, composition or volumetric restriction" (Judgment, par 88) on the operation of the tannery, despite the provisions of ss.76A and 109 of the Environmental Planning & Assessment Act.