The Policy organises its regulatory approach around several interlocking concepts: primary production as an overarching land use category; threshold‑based consent triggers; risk categorisation for aquaculture; prescribed minimum performance criteria; site and operational requirements; and instrument layering through schedules and maps.

Primary production and land use balance: The Policy states aims to facilitate orderly economic use and development for primary production and to balance primary production with residential development and protection of native vegetation, biodiversity and water resources (s 2.1(a)-(c)). That policy aim translates into concrete constraints and priorities: some land uses are permitted only with consent (sch 4 Pt 4 cl 6), clearing is restricted (cl 3.7), and prime agricultural land has special protections, including council consent requirements and a test that the development will not adversely affect other prime agricultural land (cl 3.5).

Thresholds and permissions without consent: The Policy uses quantitative and locational thresholds to distinguish low‑risk activities that do not require development consent from higher risk activities that do. Examples include:

• Small artificial waterbodies under 15 megalitres and outside specified setbacks may be carried out without consent (s 2.12).
• Routine maintenance and emergency or routine work by irrigation corporations may be carried out without consent, subject to heritage and other limitations (s 2.13-2.14).
• Temporary livestock containment and certain husbandry works may be carried out without consent subject to location restrictions (s 2.16).
• Certain pond‑based and tank‑based aquaculture can be permitted without consent where they meet Division 2 site and operational requirements in Schedule 4 Part 5 (sch 4 cl 8(4) and Part 5 requirements).

Risk taxonomy for aquaculture: Marine waters aquaculture (other than oysters) is to be subjected to a project profile analysis published in the Gazette and prepared by the Planning Secretary (s 2.24). That matrix ranks site and operational attributes across three levels of risk. The consent authority uses the matrix to form an opinion and categorise proposed development as Class 1 (all Level 1), Class 2 (Levels 1 and/or 2) or Class 3 (any Level 3) (s 2.25). Class 3 is designated development under the Act and triggers advertising and additional statutory processes (s 2.26).

Minimum performance criteria and site controls: The Policy refers to minimum performance criteria in Schedule 2 Part 2 (s 2.20(2)). For pond‑based and tank‑based aquaculture, Schedule 4 Part 5 sets detailed site location and operational requirements including conservation exclusion zones, species selection linked to aquaculture industry development plans, pond design and freshwater discharge limitations (sch 4 cls 9-19).

Mapping and lists: The Policy relies on maps and schedules to identify State significant agricultural land, priority oyster aquaculture areas, consent authorities and local environmental instruments to which these provisions apply (s 2.5; schs 1-3; sch 4 Part 6 Table). Several of those lists were blank on commencement, signalling staged implementation.

Administrative roles and consultation: Key administrative actors with statutory roles include the Planning Secretary (project profile analysis publication, s 2.24), consent authorities (including councils and the Minister where designated, ss 2.21, sch 4), and the Secretary of the Department of Industry who must be notified and consulted where development may adversely affect oyster aquaculture (s 2.27). The Policy requires consent authorities to take aquaculture industry development plans and the NSW Oyster Industry Sustainable Aquaculture Strategy into account (ss 2.22, 2.29).

Transference and savings: The Policy imports transferred provisions under the Interpretation Act 1987 s 30A (s 1.4). It provides savings for pre‑commencement development applications, which must be determined as if the Chapter had not commenced (s 2.6(1)). There is also a specific transitional savings item for applications pending before the Agritourism amendment (s 2.6(2)).

Together these concepts define a regime that mixes prescriptive minimums, discretionary consent pathways, mapping and schedule reliance, and administrative instruments that can be updated (for example project profile analyses). The remainder of this deep dive traces the effects of those mechanics on affected parties, duties and rights, enforcement, interaction with other laws, the amendment record in the text provided, litigation material in the text, practical compliance pitfalls and an implementation checklist.

The Policy assigns legal consequences and compliance obligations across a set of identifiable actors. Who pays, who decides and who changes behaviour follow from the provisions.

Primary landowners and farmers: Private landholders engaged in agriculture are directly affected. The Policy restricts clearing (cl 3.7), regulates erection of buildings, dam construction and subdivision on prime agricultural land (cl 3.5), and imposes location and operational constraints on livestock activities (s 2.16; sch 4 cl 4). Landowners proposing development may face additional consent requirements where local environmental plans are subject to Schedule 4 (Part 6 Table identifies many local EPIs) and where their land falls within mapped areas. Where the landowner wishes to create multiple dwellings on a single rural lot under a rural land sharing community, the Schedule 5 regime sets consent prerequisites and density limits, while prohibiting subdivision after approval (sch 5 cls 4-9).

Developers and aquaculture operators: Aquaculture operators are affected by the risk categorisation and minimum performance criteria. Marine waters aquaculture (except oysters) requires consent and cannot be undertaken where excluded places are identified in Schedule 2 Part 1, and consent can only be granted if minimum performance criteria in Schedule 2 Part 2 are met (s 2.20). For aquaculture outside those explicit minima, the consent authority must apply the project profile analysis in forming a categorisation (s 2.24-2.25). Designated development status for Class 3 proposals triggers advertising (s 2.26). Oyster aquaculture has special protection measures: consent authorities must consider potential adverse effects on oyster aquaculture and consult the Department of Industry Secretary if adverse effects are suspected, and may refuse consent if adverse effects cannot be avoided or minimised (ss 2.27-2.28).

Councils and consent authorities: Local councils operate as consent authorities in many situations (see Schedule 4 Part 6 Table and cl 5 Application of Part). They must apply the specific matters for consideration for intensive livestock agriculture (sch 4 cl 4(4)) and the site and operational criteria for pond and tank aquaculture (sch 4 Part 5). For Western Division large intensive livestock proposals, the Minister is the consent authority (s 2.17(5)), shifting decision responsibility away from councils to central government for those matters.

State agencies and Ministers: The Planning Secretary is required to publish project profile analyses in the Gazette for aquaculture development and to review analyses when the relevant aquaculture industry development plan is amended (s 2.24). The Secretary of the Department of Industry must be consulted on potential impacts to oyster aquaculture and the NSW Oyster Industry Sustainable Aquaculture Strategy must be considered by both consent authorities and the Department Secretary (ss 2.27, 2.29). The Minister is the consent authority where a specific consent authority is not designated in Schedule 3 (s 2.21); Schedule 3 was blank on commencement, leaving the Minister as the default consent authority for marine waters aquaculture (s 2.21(b); Schedule 3 note).

Irrigation corporations: Irrigation corporations receive a specific operational privilege. They may undertake emergency work and routine maintenance on their works without development consent on land within their area of operations, with limits for heritage and Aboriginal objects and protected areas (s 2.14). That reduces time and transaction costs for irrigation providers, while retaining environmental and cultural heritage constraints.

Water and other regulators: The Policy emphasises that development permissible without planning consent under the Policy is not exempt from approvals under other Acts, for example the Water Management Act 2000 (note to Part 2.3). Private water entitlements, licences and other regulatory permissions remain necessary where relevant.

Adjacent landowners and communities: The Policy frames locational restrictions to account for impacts on neighbours. For temporary livestock containment and goat depots allowed without consent, the Policy excludes environmentally sensitive areas, proximity to watercourses and distances from residential zones (s 2.16(2)-(3)). For intensive livestock development in the Western Division the consent authority must consider odour, water pollution and soil degradation risks (s 2.17(4)). These provisions allocate the immediate externality management tasks to proponents and consent authorities, and create potential for local opposition to consenting if impacts are not adequately mitigated.

Industry bodies and standards creators: The Department of Primary Industries (within the Department of Industry) influences outcomes through aquaculture industry development plans and through published guidelines for intensive livestock agriculture that consent authorities must have regard to (ss 2.22; s 2.17(4)(g)). Industry codes of practice and approved guidelines are specifically factored into the consent tests.

Who pays: costs are concentrated on proponents and landowners who must prepare development applications, statements of environmental effects or EIS where required; where central government is the consent authority, proponents may face higher transactional and compliance costs given ministerial processes and possible requests for additional information. Councils bear administrative costs for assessment and conditions monitoring. Irrigation corporations bear operational decision costs but obtain speed and flexibility for emergency work.

Who decides: consent authorities (councils or the Minister as designated) decide whether development proceeds. The Planning Secretary sets project profile analyses and the Department of Industry Secretary has a consultation/ advisory role where oyster aquaculture may be affected.

What behaviour changes: operators will self‑select into lower risk activities to avoid consent processes where feasible, design operations to meet minimum performance criteria and site requirements to reduce refusal risk, and, where relevant, seek to locate within priority oyster aquaculture areas to benefit from permitted‑without‑consent rules for oyster aquaculture in those areas (sch 4 cl 8(6)). Irrigation corporations will rely on emergency maintenance privileges subject to heritage and environmental constraints (s 2.14). Local councils will integrate the Policy’s matters for consideration into development assessment and condition drafting.

The Policy creates both positive duties on decision‑makers and obligations on proponents, and it preserves rights such as consultation and the ability to refuse consent where statutory tests are not met.

Duties placed on consent authorities: Consent authorities must apply statutory tests when determining applications. Examples include:

• For marine waters aquaculture, a consent authority must be satisfied the development will not be undertaken in an excluded place listed in Schedule 2 Part 1 and that it complies with minimum performance criteria in Schedule 2 Part 2 (s 2.20(2)).
• Consent authorities must take aquaculture industry development plans into consideration (s 2.22) and must have regard to the NSW Oyster Industry Sustainable Aquaculture Strategy in oyster matters (s 2.29).
• For intensive livestock agriculture under Schedule 4 Part 3, the consent authority must take into account the specified environmental and amenity matters such as odour, water pollution, soil degradation, mitigation measures, site suitability, intention to comply with animal welfare codes and consistency with Departmental guidelines (sch 4 cl 4(4)).

Duties on the Planning Secretary and Department Secretaries: The Planning Secretary must publish project profile analyses for particular aquaculture types and regions in the Gazette, ensure criteria are consistent with aquaculture industry development plans and review analyses when those plans change (s 2.24). The Secretary of the Department of Industry must be given notice where the consent authority suspects a development may adversely affect oyster aquaculture, and the consent authority must consider comments received within 21 days (s 2.27(1)-(3)). Both the consent authority and the Department Secretary must take the NSW Oyster Industry Sustainable Aquaculture Strategy into account (s 2.29).

Proponent obligations and tests: Proponents must meet the statutory thresholds and site requirements to qualify for non‑consent activity or must lodge development applications that enable consent authorities to form an opinion against the specified criteria. Key proponent duties include:

• Complying with minimum performance criteria for marine waters aquaculture (s 2.20(2)).
• Ensuring small artificial waterbodies meet capacity and setback limits to be exempt from consent (ss 2.11-2.13).
• Designing pond‑based and tank‑based aquaculture to comply with Schedule 4 site and operational requirements, such as exclusion from conservation zones, species selection consistent with aquaculture industry development plans, pond design that prevents escape, and freshwater discharge limits for intensive aquaculture (sch 4 cls 9-19).
• For rural land sharing communities, preparing operating and management arrangements and demonstrating provision for future management of water, waste, erosion, bushfire, flora and fauna as a condition of consent (sch 5 cls 4-6).

Rights and discretion for refusal: Consent authorities retain discretion and express statutory ability to refuse consent. For example, a consent authority may refuse consent if it is satisfied a development will have an adverse effect on oyster aquaculture or impede future oyster aquaculture in a priority area and appropriate measures are not proposed (s 2.28). Councils must not consent to development on prime agricultural land unless satisfied the development would not adversely affect other prime agricultural land and no viable alternative land exists for non‑agricultural purposes (cl 3.5(2)-(3)).

Procedural rights and limitations: The Policy obliges notification to the Department of Industry Secretary where oyster aquaculture may be affected but limits the time within which comments must be considered to 21 days (s 2.27(3)). Designated development remains subject to the Act’s advertising and exhibition rules, with Class 3 aquaculture development declared designated development requiring a 28‑day exhibition (s 2.26 note).

Limits on the Policy and residual rights: The Policy expressly states that development that is permissible without consent under this Part is not exempt from other statutory licences or approvals, in particular those under the Water Management Act 2000 (note to Part 2.3). It also preserves common law and neighbouring owners’ property rights. Transferred provisions are to be treated as if not transferred so far as meaning and operation are concerned (s 1.4).

Operational duties for irrigation corporations: Irrigation corporations may undertake routine maintenance and emergency work without development consent (s 2.14(1)), but they must obtain consent where routine maintenance would demolish a heritage item or Aboriginal object or occur on land with such objects or within an Aboriginal heritage place (s 2.14(3)).

Recordkeeping and map duties: The Policy requires that named maps adopted by the Chapter be kept and made available for public access according to Ministerial arrangements (s 2.5(3)). This creates an administrative duty on the Minister’s office for map availability and on proponents to check the maps.

In sum, duties are split between proponents who must meet location, operational and evidentiary tests, consent authorities that must apply specified statutory matters and consider industry plans and oyster strategy, and State officers who must publish and review profile analyses and maps. Rights include the ability for consent authorities to refuse where statutory criteria are not met and constrained timeframes for considering Department of Industry comments on oyster matters.

The Policy text supplied sets out permissions, prohibitions, and consent processes but does not itself list new penalty provisions or create unique enforcement mechanisms beyond the standard enforcement framework that applies under the Environmental Planning and Assessment Act 1979 and other relevant Acts. The Policy therefore relies on the Act’s enforcement machinery and other statutory regimes cited in the Policy for compliance and sanctioning.

Enforceability through the Act: The Policy regularly frames requirements in terms of development being permissible “only with development consent” (for example s 2.11(1); sch 4 cl 6(1)). Failure to obtain development consent where required will engage the Act’s enforcement provisions, including the Act’s powers to issue stop orders, orders to rectify unauthorised works, penalties for offences and the ability for councils and the Planning Secretary to prosecute or take remedial action. The Policy does not alter those enforcement modalities; it integrates into the Act’s existing permit and enforcement framework (s 2.4(1) notes the relationship and prevalency subject to the Act).

Prohibitions and criminal or civil consequences: The Policy specifically states that certain development is prohibited (for example pond‑based aquaculture prohibited in enumerated zones, sch 4 cl 7(1); tank‑based aquaculture prohibited in certain zones, sch 4 cl 7(2)). Undertaking prohibited development would be an unauthorised activity attracting the Act’s enforcement powers. The Policy itself does not specify the quantum of fines, but those follow from offence provisions in the Act and regulations applied to unauthorised development.

Compliance with other Acts and cross‑agency enforcement: The Policy emphasises that works permitted without planning consent are not exempt from licences or approvals under other Acts, notably the Water Management Act 2000 (note to Part 2.3) and the Fisheries Management Act 1994 for aquaculture industry development plans (s 2.2). Failure to obtain required water or fisheries licences remains enforceable under the separate Acts and their penalties. For example, water extraction or dam construction without an appropriate water licence could attract enforcement under the Water Management Act 2000.

Heritage and Aboriginal objects restrictions: The Policy imposes constraints on irrigation corporations’ emergency and routine work where heritage items or Aboriginal objects would be demolished or affected (s 2.14(3)). Undertaking demolishing works without required consents or heritage approvals may engage offences or orders under heritage and Aboriginal heritage laws. The Policy does not create separate penalty clauses for these matters; it defers to the relevant protective regimes.

Administrative remedies and refusals: The Policy expressly gives consent authorities the ability to refuse consent where statutory criteria are not satisfied, for example where aquaculture proposals do not meet minimum performance criteria (s 2.20(2)) or where development would adversely affect oyster aquaculture and appropriate avoidance or mitigation measures are not proposed (s 2.28). Refusal is an administrative enforcement outcome, and proponents may then pursue merits or judicial review under the Act if they consider the decision unlawful or unreasonable.

Monitoring obligations and public access: The Policy requires that maps and project profile analyses be published and made publicly available (s 2.5; s 2.24(1)). That public availability supports third party monitoring and potential objections, which may lead to enforcement action if unauthorised works are discovered.

Practical enforcement consequence: Because the Policy integrates with the Act rather than establishing a distinct fines regime, enforcement entails the existing Act mechanisms, with the consequence that penalty exposure will depend on the Act’s sanctioning provisions, and on whether other Acts (for example water or fisheries legislation) are also engaged. The Policy’s procedural duties such as consultation timeframes (s 2.27(3)) impose limits on when authorities must consider submissions, but the text does not create private right of action or new criminal offences distinct from the Act.

The Policy is embedded into the broader hierarchy of environmental and resource regulation. The text explicitly cross‑references multiple Acts and preserves the need to comply with those regimes.

Primacy and inconsistency: The Policy states that if there is an inconsistency between this Chapter and another environmental planning instrument, this Chapter prevails to the extent of the inconsistency, subject to section 3.28(4) of the Act (s 2.4(1)). That creates a clear rule of internal primacy among EPIs, but it remains subordinate to the Act where section 3.28(4) applies.

Interaction with the Water Management Act 2000: The Policy repeatedly notes that development permitted without planning consent under the Policy is not exempt from other approvals under other Acts, notably the Water Management Act 2000 (note to Part 2.3; definition of irrigation corporation in s 2.2). For artificial waterbodies, the Environmental Planning and Assessment Regulation 2000 continues to declare certain artificial waterbodies designated development (s 2.11 note). This means water licences, approvals for diversions, and other water law requirements remain enforceable irrespective of planning consent status.

Fisheries Management Act 1994 and aquaculture industry development plans: The Policy requires that consent authorities take aquaculture industry development plans, published under Part 6 of the Fisheries Management Act 1994, into consideration when determining aquaculture proposals (s 2.22). The project profile analyses must be consistent with the relevant aquaculture industry development plan (s 2.24(4)). Thus the Fisheries Management Act produces substantive standards that the planning consent must align with; the planning regime and fisheries regime are therefore complementary rather than substitutive.

Native vegetation, biodiversity and protected area laws: The Policy restricts clearing and identifies conservation exclusion zones where pond or tank aquaculture must not be located (sch 4 cls 9(1) and 15(1)). It references the Native Vegetation Conservation Act 1997 in defining “clear” for cl 3.7. It also excludes certain lands declared under the Biodiversity Conservation Act 2016 and Ramsar sites (sch 4 cls 9(2), 15(2)). Those references embed the Policy within the biodiversity protection framework and require proponents to remain compliant with the protective regimes governing those lands.

Heritage and Aboriginal heritage obligations: The Policy clarifies that irrigation corporations must obtain development consent where routine maintenance would demolish a heritage item or Aboriginal object, or where the work is on land where an Aboriginal object or Aboriginal place of heritage significance is located (s 2.14(3)). This cross‑references heritage protection laws and places actual limits on the otherwise broad emergency work privilege.

Local environmental plans and the Standard Instrument: The Policy treats terms used in this Chapter as having the same meaning as the Standard Instrument unless otherwise defined (s 2.2(1)) and applies certain standard provisions to a long table of non‑standard local environmental plans via Schedule 4 Part 6. That both harmonises interpretation and extends the Policy’s controls into older EPIs. Clause 2 of Schedule 4 clarifies how references to named zones should be interpreted in relation to equivalent local zones.

Other State environmental policies: The Policy expressly disapplies State Environmental Planning Policy No 1,Development Standards to aquaculture development to which Division 2 of Part 5 applies (s 2.4(2)). That removes an avenue for development standard relaxations for some aquaculture proposals, affecting the ability to seek variations under SEPP No 1 for those particular developments.

Regulatory overlap and sequential approvals: The Policy does not remove the need for approvals under other Acts. That creates sequential or parallel approvals processes , e.g. a proponent may need to obtain planning consent under the Policy, then secure water licences under the Water Management Act 2000 and aquaculture licences or leases under fisheries legislation. The Policy acknowledges that consent without these other licences does not authorise water extractions or fisheries activities.

Maps, locality and other EPIs: The Policy relies on maps that must be kept and made available (s 2.5). Where other EPIs amend or replace these named maps, the Policy accommodates those instruments approving amended maps (s 2.5(1)(b)). This mechanism embeds a multi‑instrument interaction where local instruments can amend State maps or adopt their own mapping.

In short, the Policy is designed to operate within the existing statutory landscape, using planning consent as one gate among many. It strengthens linkages with fisheries and water regimes through mandatory consideration of specific plans and retains that proponents must comply with sectoral statutes. The Policy adjusts planning discretion but does not supplant other statutory consent regimes.

The Policy text supplied contains a few express amendment annotations and repeals recorded in the margins. These amendments are internal to the provided text and show how particular clauses have been changed or schedules adjusted since commencement. The recorded amendments include:

• Section 2.6 (Savings provision relating to development applications) was amended in 2022 by State Environmental Planning Policy (Exempt and Complying Development Codes) Amendment (Agritourism) 2022, recorded as Am 2022 (593), Sch 3[1]. The provision now contains a specific savings rule requiring some development applications submitted prior to that amendment to be determined as if the Policy had not commenced (s 2.6(2) with amendment note).
• Section 2.16 (Certain development to temporarily contain livestock permissible without consent) shows amendment annotations: Am 2022 (593), Sch 3[2] [3]; 2023 No 35, Sch 2.12; 2024 (42), Sch 1.40[1]. These indicate multiple post‑commencement adjustments to thresholds, locational restrictions or the scope of that provision. The precise textual differences are not shown in separate versions here, but the annotation confirms the section has been the subject of repeated legislative updates.
• Schedule 4 amendment history: sch 4 is noted as amended by Am 2022 (593), Sch 3[4]; 2024 (42), Sch 1.40[2]-[5]; and 2025 (150), Sch 2. That indicates Schedule 4’s application to non‑standard local environmental plans has been updated multiple times.
• Schedule 5 (Rural land sharing communities) shows amendments Am 2022 (220), cl 4; 2023 (485), Sch 2. This reflects legislative changes to the rural land sharing communities provisions since their inclusion.
• Schedule 6 is recorded as repealed: Rep, 2021 (729), Sch 6.

Commencement is recorded at s 1.2: the Policy commences on 1 March 2022 and required publication on the NSW legislation website. The policy’s name is recorded in s 1.1.

Blank schedules and notes on commencement: The Policy includes several Schedules that were blank at the time Chapter 2 was made. Schedule 1 (State significant agricultural land) had no areas listed at commencement (s 2.8 note). Schedule 2 (Marine waters aquaculture minimum performance criteria and excluded places) was blank at commencement (Schedule 2 note). Schedule 3 (Designated consent authorities) was blank on commencement (Schedule 3 note). Those blanks are functionally significant; the legislature intended follow‑up instruments or maps to populate those Schedules or for other EPIs to declare maps and authorities.

The amendment notes in the text are internal markers summarising statutory amendments and repeals. They indicate the Policy has been actively adjusted since its initial making. The annotation does not provide the exact drafting history or the content of the amending instruments, but it confirms a pattern of iterative changes, particularly to livestock and Schedule 4 provisions.

The supplied Policy text does not include case law or decisions. It names no judicial determinations and does not refer to litigation. Therefore, on the basis of the text provided, there is no litigation history to report. The Policy does reference statutory instruments and plans that have been the subject of administrative processes and may in practice generate litigation, but the text itself contains no recorded judicial pronouncements or litigation citations.

When assessing potential litigation risk in practice, users should note that the Policy intersects with the Environmental Planning and Assessment Act 1979 and other statutes that have established judicial review and merits appeal routes, and that issues likely to generate litigation include: (a) classification disputes under the project profile analysis for aquaculture (ss 2.24-2.26), (b) whether minimum performance criteria have been satisfied (s 2.20(2)), (c) consistency with aquaculture industry development plans and the NSW Oyster Industry Sustainable Aquaculture Strategy (ss 2.22, 2.29), (d) whether a proposed development is within conservation exclusion zones or prime agricultural land and thus prohibited or restricted (sch 4 cls 9, 15; cl 3.5), and (e) whether emergency or routine works by irrigation corporations were lawfully executed without consent (s 2.14). However, such litigation examples are hypothetical consequences implied by the Policy’s structure; no cases are cited in the Policy text supplied.

Practitioners should, for a litigation risk assessment, review subsequent decisions of consent authorities and any judicial review cases post‑commencement that interpret the Policy, the project profile analysis matrices, and the interface with the Fisheries Management Act 1994 and Water Management Act 2000. Those materials fall outside the text provided and are not included here.

The Policy’s practical application contains several points that commonly cause compliance surprises. These "gotchas" are grounded in the Policy wording and its dependency on other instruments.

Blank Schedules and maps create initial uncertainty: Schedule 1 (State significant agricultural land), Schedule 2 (marine waters aquaculture excluded places and minimum performance criteria) and Schedule 3 (designated consent authorities) were blank on commencement (s 2.8 note; Schedule 2 note; Schedule 3 note). Until those lists and maps are populated, proponents and consent authorities may face uncertainty about whether the State has identified particular lands or consent arrangements, or what minimum criteria apply. In the absence of a named consent authority in Schedule 3, the Minister remains the default consent authority for marine waters aquaculture (s 2.21(b)). Proponents should check whether subsequent instruments have populated these Schedules or whether local EPIs have declared replacement maps.

Savings provision can reverse expectations: The Policy requires that development applications made before its commencement and not finally determined must be determined as if the Chapter had not commenced (s 2.6(1)). That means that an application lodged before 1 March 2022 may avoid the new Chapter’s requirements even though the policy is now in force. Practitioners must check lodgement dates carefully; relying on current policy for design may be unnecessary where an earlier application remains pending.

Non‑planning approvals remain necessary: The Policy repeatedly notes that development permissible without planning consent is not exempt from other approvals, notably water approvals under the Water Management Act 2000 (note to Part 2.3). Practitioners must not assume that a “no consent needed” planning outcome obviates water licensing, fisheries licences or other sectoral consents.

Irrigation corporation emergency work privilege has limits: Irrigation corporations can perform routine and emergency maintenance without development consent (s 2.14(1)), but the privilege is subject to other environmental planning instruments (s 2.14(2)) and does not apply where routine maintenance would demolish a heritage item or an Aboriginal object or be on land with such objects (s 2.14(3)). Assuming unfettered authority for urgent works can be a risk where heritage values are present.

SEPP No 1 does not apply to some aquaculture: The Policy disapplies State Environmental Planning Policy No 1 to aquaculture development to which Division 2 of Part 5 applies (s 2.4(2)). This removes an avenue for concession on development standards for those aquaculture developments, which may catch proponents expecting to seek variations under SEPP No 1.

Project profile analysis is administrative and may change: The project profile analysis that categorises aquaculture risk is published by the Planning Secretary and must be reviewed when the aquaculture industry development plan is amended (s 2.24(1), (5)). That gives rise to regulatory change risk: a proponent who designs a project to fit a particular classification may find the matrix altered on plan amendment. The Policy empowers the Planning Secretary to determine classification criteria, creating an administrative discretion step practitioners must monitor.

Oyster consultation time limit: Where a consent authority gives notice to the Secretary of the Department of Industry about a suspected adverse effect on oyster aquaculture, comments received more than 21 days after notice need not be considered (s 2.27(3)). If a Department response is delayed, consent authorities can discount later submissions. Practitioners should not assume indefinite consultation windows.

Default to Minister for some aquaculture consents: Because Schedule 3 was blank on commencement, the Minister is the default consent authority for marine waters aquaculture absent a designated consent authority (s 2.21(b); Schedule 3 note). This can lengthen assessment timelines and change the appeals and referral pathways practitioners expect compared to local council control.

Rural land sharing communities: While Schedule 5 enables multiple dwellings on a single lot without subdivision, the Schedule prohibits subsequent subdivision of the land once such development has occurred (sch 5 cl 8). That structural constraint can surprise purchasers who expect to convert communal arrangements into separate titles later. Density caps and a prohibition on certain tourist or caravan uses also constrain commercial re‑purposing (sch 5 cls 4(1)(e), 7).

Intensive livestock thresholds and locational rules: Intensive livestock agriculture is permitted without consent below specified capacity thresholds in many EPIs (sch 4 cl 4(6)), but the exemptions are conditional on not being in environmentally sensitive areas, not being within specified distances of watercourses or dwellings, and in drinking water catchments (sch 4 cl 4(5)-(6)). Misreading these distance‑based exclusions is a frequent compliance trap. The Western Division has separate thresholds and the Minister is the consent authority for larger operations (s 2.17(2)-(5)).

Designated development advertising and EIS obligations: Classification of aquaculture as Class 3 leads to designated development status and statutory advertising and assessment requirements (s 2.26 note). Proponents should not assume an expedited path where the project profile analysis indicates any Level 3 attribute.

Overall, the principal practical gotchas are the need to check pre‑commencement application status, to secure non‑planning approvals (water, fisheries), to monitor the Planning Secretary’s project profile analyses and map publications, and to recognise the special rules and constraints that apply to oysters, irrigation corporations and rural land sharing communities.

This section translates the Policy text into an operational checklist and practical steps for proponents, consent authorities and advisers. It groups compliance tasks by activity type and highlights documents, timeframes and decision‑makers to consult.

Initial triage and mapping

1. Determine whether the land falls within the Chapter or a specific Part: check s 2.3 (Chapter applies to the State unless otherwise provided) and schedule‑mapped areas such as East Cadell Map for Part 2.3 work (s 2.10). Use the Ministerially approved maps kept under s 2.5 and any amendments published by environmental planning instruments.
2. Check whether a development application was lodged before 1 March 2022 and remained undetermined. If so it should be determined as if this Chapter had not commenced (s 2.6(1)). For specific agritourism amendments, see s 2.6(2).

For artificial waterbodies (dams, storages)

1. Measure intended storage capacity. If capacity is less than 15 megalitres and the dam is not within 40 metres of a public road, a natural waterbody, an environmentally sensitive area or tree clearing operations, the work may proceed without development consent (s 2.12).
2. If storage capacity is between 15 and 100 megalitres and in an environmentally sensitive area, or 800 megalitres or greater in irrigation areas, the Environmental Planning and Assessment Regulation 2000 may declare the works designated development, requiring consent and possible EIS (s 2.11 and note). Confirm designated development status in the Regulation.
3. Obtain any water licences or approvals under the Water Management Act 2000 as required. The Policy does not replace those approvals (note to Part 2.3).

For irrigation corporations carrying out maintenance or emergency work

1. Confirm that the works are within the corporation’s area of operations and qualify as routine maintenance or emergency work as defined (s 2.14(1) and definition of emergency work).
2. Check for any other environmental planning instrument that declares the development exempt or prohibits it; the s 2.14(1) privilege does not apply where other instruments exempt or prohibit the work (s 2.14(2)).
3. If routine maintenance would demolish a heritage item or an Aboriginal object or occur on land with those features, obtain development consent instead (s 2.14(3)).

For livestock and temporary containment

1. Confirm land is an agricultural land where such development may be carried out with or without consent (s 2.16(1)).
2. For temporary stock containment, verify that the location is not in an environmentally sensitive area, not within 100 metres of a special area under the Water NSW Act 2014, not within 100 metres of a natural watercourse, and not within 500 metres of a residential zone or residential accommodation on adjacent land (s 2.16(2)(c)). Goat depots have the same absolute locational prohibitions (s 2.16(3)).
3. Prepare documentation demonstrating emergency circumstances or routine husbandry purpose, and evidence of lawful agricultural use of the land where required (s 2.16(2)(b)).

For intensive livestock agriculture in the Western Division

1. Determine whether the land falls within the Western Division and not within a local government area (s 2.17(1)).
2. If capacity thresholds are exceeded (for example cattle feedlot 50+ head, pig farm 200+ pigs or 20+ breeding sows), lodge development application because consent is required (s 2.17(2)).
3. Prepare environmental assessments addressing odour, potential water pollution, soil degradation, mitigation measures, site suitability, animal welfare codes of practice adherence, and consistency with Department of Primary Industries guidelines, as these are mandatory considerations (s 2.17(4)).
4. Be aware the Minister is the consent authority for these applications (s 2.17(5)).

For marine waters aquaculture (other than oysters)

1. Identify whether the development is to be carried out in an excluded place in Schedule 2 Part 1. If excluded, development must not be undertaken (s 2.20(2)(a)).
2. Obtain and review the project profile analysis published by the Planning Secretary for the aquaculture type and region. The project profile analysis will provide the risk matrix used to classify the proposal into Class 1, 2 or 3, per ss 2.24-2.25.
3. Ensure the proposal complies with minimum performance criteria set out in Schedule 2 Part 2. Consent must not be granted unless the authority is satisfied of compliance (s 2.20(2)(b)).
4. Determine the consent authority from Schedule 3; if none is designated, the Minister is the consent authority (s 2.21).
5. If the proposal is Class 3, prepare for designated development processes including 28‑day advertising and potentially an EIS (s 2.26 note).

Oyster aquaculture specific steps

1. Before deciding any development application, the consent authority must consider whether the development may adversely affect oyster aquaculture or a priority oyster aquaculture area (s 2.27(1)(a)).
2. If there is a suspicion of adverse effect, give notice to the Secretary of the Department of Industry and consider any comments received within 21 days (s 2.27(1)(b); (3)).
3. Consider comments that identify adverse effects and measures to avoid or minimise them, and the NSW Oyster Industry Sustainable Aquaculture Strategy (s 2.27(2); s 2.29).
4. Be prepared to refuse consent where the consent authority is satisfied that appropriate measures to avoid or minimise adverse effects are not proposed (s 2.28).

For pond‑based and tank‑based aquaculture and pond design

1. Confirm the zone in which the proposal sits: Schedule 4 cl 6 limits where pond‑based and tank‑based aquaculture may proceed only with consent in specified equivalent zones.
2. Ensure site location requirements such as conservation exclusion zones are satisfied (sch 4 cls 9, 15).
3. Comply with operational requirements: species selection consistent with aquaculture industry development plans (sch 4 cls 10, 17), pond design allowing full drainage and drying for intensive pond aquaculture (sch 4 cl 11), discharge rules for freshwater from intensive aquaculture (sch 4 cl 12), and screens on outlets to prevent fish escape (sch 4 cl 13).
4. If extensive pond‑based aquaculture is proposed to be carried out without consent in specified rural zones, ensure compliance with Division 2 site and operational requirements (sch 4 cl 8(4) and Part 5).

Rural land sharing communities

1. Check the land is in a rural zone and not excluded categories under sch 5 cl 3.
2. Prepare an application demonstrating the lot is a single lot with area not less than 10 hectares and meets building height, prime crop limitations and slope/ hazard criteria (sch 5 cl 4).
3. Prepare operating and management arrangements and evidence of future management provisions for water and waste, soil erosion control, bushfire management, flora and fauna management, and maintenance of internal infrastructure (sch 5 cls 5-6).
4. Ensure the proposed number of dwellings is within Schedule 5 density limits and does not result in persons accommodated exceeding the permitted multiples (sch 5 cl 7).
5. Note that subdivision is prohibited once development under this Schedule has been carried out (sch 5 cl 8).

Administrative and documentary matters

1. Check all relevant maps and project profile analyses published under s 2.24 and s 2.5, and the aquaculture industry development plans required by the Fisheries Management Act 1994.
2. Prepare statements of environmental effects or environmental impact statements as required under the Act and the Regulation. For designated development determinations, expect exhibition and public participation steps (s 2.26 note).
3. If the Department of Industry is consulted on oyster impacts, anticipate a 21‑day window for the Department to provide comments that the consent authority must consider if received in time (s 2.27(3)).
4. Record compliance with minimum performance criteria and Schedule 4 operational requirements to demonstrate to the consent authority that statutory tests are met (s 2.20(2)).

Monitoring and post‑approval obligations

1. For consents granted, ensure conditions reflect site and operational controls set out in Schedule 2 and Schedule 4; these are minimum requirements and consent authorities may impose stricter conditions (s 2.20(3); sch 4 cl 8(3)).
2. For irrigation corporations executing emergency work without consent, document the emergency circumstances and any heritage or Aboriginal object checks, particularly where s 2.14(3) would otherwise require consent.
3. Maintain records of species selection and operation consistent with aquaculture industry development plans and any monitoring required by consent conditions (sch 4 cl 10 and cl 17).

Checklists for advisers

• Confirm jurisdictional maps and whether applicable Schedules have been populated since commencement.
• Obtain and review the relevant aquaculture industry development plan and the NSW Oyster Industry Sustainable Aquaculture Strategy where aquaculture or oyster issues arise (ss 2.22, 2.29).
• Identify whether the proposal is likely Class 3 on the project profile analysis to prepare for EIS and advertising (ss 2.24-2.26).
• For rural land sharing community projects, ensure governance and management arrangements are legally enforceable, for example by consent conditions, covenants or management agreements (sch 5 cl 5-6).

This compliance approach follows directly from the statutory text. Practitioners should always confirm whether the blank Schedules and maps have been populated or amended post‑commencement, and should cross‑check any other EPIs and the Environmental Planning and Assessment Regulation 2000 for designated development declarations referenced in the Policy notes.