Water Sharing Plan for the Bellinger River Area Unregulated and Alluvial Water Sources 2008 (NSW)
This Plan is the Water Sharing Plan for the Bellinger River Area Unregulated and Alluvial Water Sources 2008 (hereafter
This Plan is made under section 50 (1A) of the Water Management Act 2000 (hereafter
This Plan is a plan for water sharing, and covers the provisions of sections 20 (1), 20 (2) (a) to 20 (2) (e), 20 (3), 20 (4), 21 (a) to 21 (c) and 21 (f) of the Act and dispenses with section 16 of the Act.
This Plan takes effect on 1 July 2008 and ceases 10 years after that date.
The area in respect of which this Plan is made is that area of land within part of the Upper North Coast Water Management Area, known as the Bellinger River Area Unregulated and Alluvial Water Sources (hereafter
These water sources exclude the area of land below the mangrove limit.
The mangrove limit is as defined in the DIPNR Survey of tidal limits and mangrove limits in NSW estuaries 1996 to 2003 (NSW Dept of Commerce, Manly Hydraulics Laboratory).
These water sources in respect of which this Plan is made, and shown on the plan map called Plan Map (WSP0002_Version 1). Water Sharing Plan for the Bellinger River Area Unregulated and Alluvial Water Sources 2008 (hereafter
(a) Bellinger River Water Source,
(b) Boggy Creek Water Source,
(c) Coastal Bellinger Water Source,
Note— This water source excludes alluvial groundwater downstream of the tidal limits.
(d) Coastal Kalang Water Source,
Note— This water source excludes alluvial groundwater downstream of the tidal limits.
(e) Dalhousie Creek Water Source,
(f) Hydes Creek Water Source,
Note— This water source excludes alluvial groundwater downstream of the tidal limits.
(g) Kalang River Water Source,
Note— This water source excludes alluvial groundwater downstream of the tidal limits.
(h) Never Never Creek Water Source,
(i) Rosewood Creek Water Source,
(j) Spicketts Creek Water Source, and
(k) Thora–North Arm Bellinger River Water Source.
The Plan Map is part of this Plan. An overview of these water sources is shown in Appendix 1. The Plan Map referred to in this Plan may be inspected at offices listed in Appendix 2 and is available at the NSW Legislation website.
The Thora–North Arm Bellinger River Water Source is divided into the following management zones and shown on the Plan Map:
(a) Upper Thora–North Arm Bellinger River Management Zone, and
(b) Lower Thora–North Arm Bellinger River Management Zone.
The Bellinger River, Hydes Creek, Kalang River, Coastal Bellinger and Coastal Kalang Water Sources are divided into the following management zones:
(a) Non Tidal Management Zone, and
(b) Tidal Pool Management Zone.
The Minister may under section 45 (1) (b) of the Act amend subclauses (1), (2) and (3) to amend an existing water source or management zone, or establish a new or additional management zones.
Following an amendment to or the establishment of a water source, management zone or management zones under subclause (4) the Plan Map may be amended.
The waters of these water sources include:
(a) all water occurring on the land surface shown on the Plan Map, including but not limited to all rivers, lakes and wetlands in these water sources, and
(b) all groundwater within all alluvial sediments below the surface of the land on the Plan Map, excluding:
(i) any alluvial sediments downstream of the tidal limit, excluding the Bellinger River within the Bellinger River Water Source,
Note— This exclusion applies to part of the Hydes Creek, Kalang River, Coastal Bellinger and Coastal Kalang Water Sources.
(ii) any groundwater contained in the coastal sands, and
(iii) any groundwater contained in fractured rock aquifers and basement rocks in the area to which this Plan applies.
Note— Alluvial groundwater and surface water in water sources with highly connected surface and groundwaters are treated as a single ‘resource’ within this Plan. Therefore, traditional management of groundwater via sustainable yield and extraction limits is not used within these water sources. Instead, management of surface and groundwater may be linked to surface water flow or groundwater levels. Note however, that this only applies to ‘highly’ connected alluvial groundwater. Alluvial groundwater that is not contained in the specified water sources is addressed under the Coastal Alluvial Groundwater Sharing Plan (
currently under development ).
Terms that are defined in the Act have the same meaning in this Plan and the effect of these terms may be explained in Notes.
Additional terms to those identified in subclause (1) are defined in Schedule 1.
Notes in the text of this Plan do not form part of this Plan.
Schedules to this Plan form part of this Plan.
Appendices to this Plan do not form part of this Plan.
This Plan applies from the date of commencement to those matters that are administered under the Act at that time.
This Plan applies to other matters from the date the relevant provisions of the Act are commenced.
This Plan is consistent with the State Water Management Outcomes Plan published in the Gazette on 20 December 2002 (hereafter
The State Water Management Outcomes Plan published in the Gazette on 20 December 2002 has expired and has not been replaced.
This part is made in accordance with section 35 (1) of the Act.
The vision of this Plan is to provide healthy and enhanced water dependant ecosystems and equitable water sharing among users in the Bellinger River Area Unregulated and Alluvial Water Sources.
The objectives of this Plan are to:
(a) protect, preserve, maintain or enhance the important river flow dependent and high priority groundwater dependent ecosystems of these water sources,
(b) protect, preserve, maintain or enhance the Aboriginal, cultural and heritage values of these water sources,
(c) protect basic landholder rights,
(d) manage these water sources to ensure equitable sharing between users,
(e) provide opportunities for market based trading of access licences and water allocations within sustainability and system constraints,
(f) provide sufficient flexibility in water account management to encourage responsible use of available water,
(g) contribute to the maintenance of water quality,
(h) provide recognition of the connectivity between surface water and groundwater, and
(i) adaptively manage these water sources.
For the purposes of the Inter-government Agreement on the National Water Initiative (2004) the environmental and other public benefit outcomes are:
1. the important river flow dependent environmental, Aboriginal, cultural and heritage values of these water sources are protected, preserved, maintained or enhanced,
2. these water sources are managed to ensure equitable sharing between users,
3. basic landholder rights of owners, or occupiers, of land are protected, and
4. the maintenance of water quality contributed to.
The strategies of this Plan are to:
(a) establish environmental water rules,
(b) identify water requirements for basic landholder rights,
(c) identify water requirements for access licences,
(d) establish rules for granting of access licences and approvals,
(e) establish rules that place limits on the availability of water for extraction,
(f) establish rules for making available water determinations,
(g) establish rules for the operation of water accounts,
(h) establish rules which specify the circumstances under which water may be extracted,
(i) establish access licence dealing rules,
(j) establish performance indicators, and
(k) identify triggers for and limits to changes to the rules.
The following indicators are to be used to determine the performance of this Plan against its objectives:
(a) change in low flow regime,
(b) change in moderate to high flow regime,
(c) change in groundwater extraction relative to the long-term average annual extraction limit,
(d) change in local water utilities access,
(e) change in, or maintenance of, ecological value of key water sources and their dependent ecosystems,
(f) extent to which basic landholder rights requirements have been met,
(g) extent to which local water utility requirements have been met,
(h) extent to which native title rights requirements have been met,
(i) change in economic benefits derived from water extraction and use, and
(j) extent of recognition of spiritual, social, economic and customary values of water to Aboriginal people.
This Part is made in order to give effect to section 5 (3) of the Act, and in accordance with sections 20 (2) (a) and 20 (2) (c) of the Act.
This Plan recognises climatic variability and therefore river flow and groundwater level variability in these water sources.
To give effect to subclause (1), this Plan has provisions that manage:
(a) the sharing of water in these water sources within the limits of water availability on a long-term average annual basis,
(b) the sharing of flows that occur in specified water sources on a daily basis, and
(c) water extraction to maintain groundwater dependent ecosystems.
The availability of water for extraction from these water sources on a long-term average annual basis will be determined at the level of an extraction management unit.
The extraction management units of which these water sources are part are known as the Bellinger River Catchment Extraction Management Unit and the Dalhousie Creek Catchment Extraction Management Unit, and are shown on the Plan Map.
The Bellinger River Catchment Extraction Management Unit consists of the following water sources:
(a) Bellinger River Water Source,
(b) Boggy Creek Water Source,
(c) Coastal Bellinger Water Source,
(d) Coastal Kalang Water Source,
(e) Hydes Creek Water Source,
(f) Kalang River Water Source,
(g) Never Never Creek Water Source,
(h) Rosewood Creek Water Source,
(i) Spicketts Creek Water Source, and
(j) Thora–North Arm Bellinger River Water Source.
The Dalhousie Creek Catchment Extraction Management Unit consists of the Dalhousie Creek Water Source.
Subject to clause 19, for the purposes of this Plan all flows referred to relate to the measured flows at the flow reference points for each water source or management zone specified in clause 18.
The Minister may under Section 45 (1) (b) of the Act amend the flow reference point for the Boggy Creek Water Source, if following a hydrologic study the Very Low Flow Class is found to be less than visible flow at the end of the system under clause 18 (2) (a) of this Plan.
The Minister may under Section 45 (1) (b) of the Act amend the flow reference point for the Boggy Creek Water Source, following the establishment of a gauge for the B Class flows under clause 18 (2) (d) of this Plan.
The Minister may under Section 45 (1) (b) of the Act amend the flow reference point for the Coastal Bellinger Water Source, the Bellinger River Water Source, the Rosewood Creek Water Source, the Never Never Water Source and the Boggy Creek Water Source, if a gauge is installed downstream of the junction of the Bellinger River and Roses Creek, and the site is found suitable as a flow reference point for the individual water sources under clause 18 (2) (b) of this Plan.
The Plan Map may be amended by the Minister under section 45 (1) (b) of the Act as a result of the establishment of, or changes to, flow reference points under subclauses (2), (3) and (4), and clause 18 (2) of this Plan.
This Plan establishes the following flow classes as the basis for sharing of daily flows from these water sources:
The following flow classes apply to all access licences extracting from surface water specified for each water source from the commencement date of this Plan, excluding those access licences listed under clause 64 and access licences that nominate a runoff harvesting dam. They will also apply to all existing aquifer access licence holders extracting from alluvial aquifers within 40 metres of the high bank of the river from year six of this Plan. For those aquifer access licences outside the 40 metres daily flow classes will not apply, except where provided under clause 65 (2) of this Plan.
(a) for the Non Tidal Management Zone of the Bellinger River Water Source, at the Bellinger River gauge at Thora in the Thora–North Arm Bellinger River Water Source:
(i) the Very Low Flow Class is when flows are at or below 16 megalitres per day (hereafter
ML/day ),Note— 16 ML/day corresponds to the estimated 95
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) A Class is when flows are greater than 16 ML/day and less than 95 ML/day, and
Note— 95 ML/day corresponds to the estimated 50
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(iii) B Class is when flows are equal or greater than 95 ML/day,
Note— B Class relates to unregulated river (subcategory “Aboriginal community development”) access licences.
Note— These flow classes may be amended if a gauging station is installed within or close to the water source, in accordance with clause 18 (2) (b) of this Plan.
(b) for the Tidal Pool Management Zone of the Bellinger River Water Source, at the Bellinger River gauge at Thora in the Thora–North Arm Bellinger River Water Source:
(i) the Very Low Flow Class is when flows are at or below 16 ML/day,
Note— 16 ML/day corresponds to the estimated 95
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) A Class is when flows are greater than 16 ML/day and less than 95 ML/day, and
Note— 95 ML/day corresponds to the estimated 50
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(iii) B Class is when flows are equal or greater than 95 ML/day,
Note— B Class relates to unregulated river (subcategory “Aboriginal community development”) access licences.
Note— These flow classes may be amended if a gauging station is installed within or close to the water source, in accordance with clause 18 (2) (b) of this Plan.
Note— These flow classes may be amended during the life of this Plan based on the outcome of a review of existing hydrological and ecological studies, and salinity monitoring, in accordance with clause 18 (2) (f) of this Plan.
(c) for the Boggy Creek Water Source, at the Bellinger River gauge at Thora in the Thora–North Arm Bellinger River Water Source:
(i) the Very Low Flow Class is when flows are at or below 16 ML/day, and
Note— 16 ML/day corresponds to the estimated 95
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) A Class is when flows are greater than 16 ML/day,
Note— These flow classes may be amended based on the outcomes of a hydrological study of end of system flows, in accordance with clause 18 (2) (a) of this Plan.
Note— These flow classes may be amended if a gauging station is installed within or close to the water source, in accordance with clause 18 (2) (b) of this Plan.
Note— These flow classes may be amended if an unregulated river (subcategory “Aboriginal community development”) access licence is granted in this water source, in accordance with clause 18 (2) (d) and 18 (2) (e) of this Plan.
(d) for the Non Tidal Management Zone of the Coastal Bellinger Water Source, no flow classes are established for this Plan,
(e) for the Tidal Pool Management Zone of the Coastal Bellinger Water Source, at the Bellinger River gauge at Thora in the Thora–North Arm Bellinger River Water Source:
(i) the Very Low Flow Class is when flows are at or below 16 ML/day,
Note— 16 ML/day corresponds to the estimated 95
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) A Class is when flows are greater than 16 ML/day and less than 95 ML/day, and
Note— 95 ML/day corresponds to the estimated 50
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(iii) B Class is when flows are equal or greater than 95 ML/day,
Note— B Class relates to unregulated river (subcategory “Aboriginal community development”) access licences.
Note— These flow classes may be amended if a gauging station is installed within or close to the water source, in accordance with clause 18 (2) (b) of this Plan.
Note— These flow classes may be amended during the life of this Plan based on the outcome of a review of existing hydrological and ecological studies, and salinity monitoring, in accordance with clause 18 (2) (f) of this Plan.
(f) for the Non Tidal Management Zone of the Coastal Kalang Water Source, no flow classes are established for this Plan,
Note— Flow classes may be established if an unregulated river (subcategory “Aboriginal community development”) access licence is granted in this water source, in accordance with clause 18 (2) (e) of this Plan.
(g) for the Tidal Pool Management Zone of the Coastal Kalang Water Source, at the Sunny Corner Road crossing in the Kalang River Water Source:
(i) for the first five years of this Plan, the Very Low Flow Class is when flows are at or below 2 ML/day, thereafter the Very Low Flow Class is when flows are at or below 4 ML/day,
Note— 2 ML/day corresponds to the estimated 99.5
th percentile and 4 ML/day corresponds to the estimated 98th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) for the first five years of this Plan, A Class is when flows are greater than 2 ML/day, thereafter A Class is when flows are greater than 4 ML/day,
Note— These flow classes may be amended if an unregulated river (subcategory “Aboriginal community development”) access licence is granted in this water source, in accordance with clause 18 (2) (e) of this Plan.
Note— These flow classes may be amended during the life of this Plan based on the outcome of a review of existing hydrological and ecological studies, and salinity monitoring, in accordance with clause 18 (2) (f) of this Plan.
(h) for the Dalhousie Creek Water Source, no flow classes are established for this Plan,
(i) for the Non Tidal and Tidal Pool Management Zones of the Hydes Creek Water Source, at Kethels Road bridge:
(i) the Very Low Flow Class is when flows are at or below 1 ML/day, and
Note— 1 ML/day corresponds to the estimated 95
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) A Class is when flows are greater than 1 ML/day,
Note— These flow classes may be amended if an unregulated river (high flow) access licence or unregulated river (subcategory “Aboriginal community development”) access licence is granted in this water source, in accordance with clause 18 (2) (e) of this Plan.
Note— These flow classes may be amended during the life of this Plan based on the outcome of a review of existing hydrological and ecological studies, and salinity monitoring, in accordance with clause 18 (2) (f) of this Plan.
(j) for the Non Tidal and Tidal Pool Management Zones of the Kalang River Water Source, at the Sunny Corner Road crossing:
(i) for the first five years of this Plan, the Very Low Flow Class is when flows are at or below 2 ML/day, thereafter the Very Low Flow Class is when flows are at or below 4 ML/day,
Note— 2 ML/day corresponds to the estimated 99.5
th percentile and 4 ML/day corresponds to the estimated 98th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) for the first five years of this Plan, A Class is when flows are greater than 2 ML/day, thereafter A Class is when flows are greater than 4 ML/day,
(k) for the Never Never Creek Water Source, at Promised Land Loop Road, immediately upstream of the Arthur Keogh Reserve:
(i) the Very Low Flow Class is when flows are at or below 2 ML/day, and
Note— 2 ML/day corresponds to the estimated 95
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) A Class is when flows are greater than 2 ML/day,
Note— These flow classes may be amended if a gauging station is installed within or close to the water source, in accordance with clause 18 (2) (b) of this Plan.
Note— These flow classes may be amended if an unregulated river (high flow) access licence is granted in this water source, in accordance with clause 18 (2) (e) of this Plan.
(l) for the Rosewood Creek Water Source, at the Bellinger River gauge at Thora in the Thora–North Arm Bellinger River Water Source:
(i) the Very Low Flow Class is when flows are at or below 16 ML/day, and
Note— 16 ML/day corresponds to the estimated 95
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) A Class is when flows are greater than 16 ML/day,
Note— These flow classes may be amended if a gauging station is installed within or close to the water source, in accordance with clause 18 (2) (b) of this Plan.
(m) for the Spicketts Creek Water Source, no flow classes are established for this Plan, and
Note— Flow classes may be established if an unregulated river (subcategory “Aboriginal community development”) access licence is granted in this water source, in accordance with clause 18 (2) (e) of this Plan.
(n) for the Thora–North Arm Bellinger River Water Source, at the Bellinger River gauge at Thora:
(i) the Very Low Flow Class is when flows are at or below 16 ML/day, and
Note— 16 ML/day corresponds to the estimated 95
th percentile. The percentiles refer to lowest flow month at the gauge and include all days of record.(ii) A Class is when flows are greater than 16 ML/day.
The Minister may under section 45 (1) (b) of the Act amend subclauses (1) (a), (1) (b), (1) (c), (1) (e), (1) (f), (1) (g), (1) (i), (1) (j), (1) (k), (1) (l) and (1) (m) to amend or establish a new or additional flow class or flow classes in:
(a) the Boggy Creek Water Source, if following a hydrologic study the bottom of A Class is found to be less than visible flow at the end of the water source, then the flow classes will change to ensuring extraction of water from a river by an approved water supply work is permitted if there is a visible flow in the river in the downstream vicinity of the water supply work, or where water is being taken from a pool, a visible inflow and outflow to and from that pool,
(b) the Tidal Pool Management Zone of the Coastal Bellinger Water Source, the Bellinger River Water Source, the Rosewood Creek Water Source, the Never Never Water Source and the Boggy Creek Water Source, if a gauge is installed near the junction of the Bellinger River and Roses Creek and sufficient data collection to enable determination of a cease to pump level at the flow reference point at or below the equivalent to the 95
th percentile flow at the end of the management zone,(c) the Coastal Bellinger and the Coastal Kalang Water Sources if a Drainage Management Plan, Floodplain Management Plan or similar management plan is developed for all or part of the water sources,
(d) the Boggy Creek Water Source, if an unregulated river (subcategory “Aboriginal community development”) access licence is granted under clause 35 (2) (f), a gauge may be installed in Boggy Creek and calibrated to the equivalent of a flow that is equal to the 50
th percentile daily flow for the B Class,Note— The percentiles refer to lowest flow month at the gauge and include all days of record.
(e) the Boggy Creek Water Source, the Coastal Kalang Water Source, the Hydes Creek Water Source, the Never Never Creek Water Source and the Spicketts Creek Water Source, if an unregulated river access licence is converted to an unregulated river (high flow) access licence under clause 74 (2), or an unregulated river (subcategory “Aboriginal community development”) access licence is granted under clause 35 (2) (f), such that B Class is when flows are greater than a flow that is equal to the 50
th percentile daily flow, andNote— The percentiles refer to lowest flow month at the gauge and include all days of record.
(f) the Tidal Pool Management Zones of the Bellinger River, the Coastal Bellinger, the Coastal Kalang and the Hydes Creek Water Sources, during the life of this Plan, based on a review of salinity monitoring, and ecological and hydrological studies to determine whether the Very Low Flow Classes are under or over satisfying ecological needs in the tidal pool, within the range in variation between visible flow and the 95
th percentile at the nominated flow reference point or a salinity threshold equivalent.
If in the Minister’s opinion, on any day accurate flow data is not available from a flow measuring gauge used to determine a flow class specified in clause 18 (1), the Minister may determine the flow class that applies for that day and notify the licence holder in writing, the flow class that applies for that day. For the purpose of this clause, notification includes publishing a notice on the Department’s website.
There is a general requirement for holders of water supply work approvals to record in a Logbook, where one is required to be kept, a confirmation and means of confirmation that the relevant cease to take conditions do not apply before taking water. Holders of access licences may contact the Department’s Grafton office at the address listed in Appendix 2 or check the Department’s website to find out what flow class applies that day and note this as required in the Logbook. In determining whether access to water is permitted that day, the Minister may take into consideration evidence of past and current flows and readings at other functioning gauges.
This Part is made in accordance with sections 5 (3) and 8 (1), 8 (1A), 8 (2), 8 (4), 8A, 8B, 8C, 8D, 8E and 20 (1) (a) of the Act.
Planned environmental water is identified and established in these water sources as follows:
(a) water volume in excess of the respective long-term average annual extraction limit established in clause 42 of this Plan may not be taken and used for any purpose in these water sources, thereby protecting a proportion of river flows for fundamental ecosystem needs from increases in long-term water extraction, and
(b) for all water sources, the water remaining in the water source after taking water to meet basic landholder rights and for access licences in accordance with the rules identified in clause 21 (3).
The planned environmental water established in clause 21 (1) (a) for these water sources is maintained by the rules in clause 44 that limit the availability of water for extraction under access licences, thereby protecting a proportion of natural river flows for fundamental ecological needs from increases in long-term water extraction.
Subject to subclause (5), the planned environmental water established in clause 21 (1) (b) is maintained as follows:
(a) subject to paragraph (g), water must not be taken under an access licence with a share component that specifies a water source or an extraction component that specifies a management zone with a Very Low Flow Class that has commenced, when flows are in the relevant Very Low Flow Class,
Note— Water sources and management zones with a Very Low Flow Class are specified in clause 18.
(b) subject to paragraph (g), water must not be taken under an access licence where a cease to take condition that was specified on the Water Act 1912 entitlement that the access licence replaces is, in the Minister’s opinion, higher than:
(i) the upper limit of the relevant Very Low Flow Class (as specified in clause 18), or
(ii) the access rule specified in paragraph (c),
when flows are at or less than the cease to take condition that was specified on the replaced Water Act 1912 entitlement,
(c) subject to paragraph (g), an access licence must not be used to take water:
(i) if there is no visible flow in the water source at the location at which water is proposed to be taken, or
(ii) where water is being taken from a pool, if there is no visible inflow and outflow to and from that pool,
(d) subject to paragraph (g), water must not be taken under an access licence with a share component that specifies the Bellinger River Water Source for more than 8 hours per day when the flow of water in the Bellinger River at the Bellinger River at Thora gauge is greater than 16 ML/day and less than or equal to 32 ML/day,
(e) subject to paragraph (g), water must not be taken under an access licence with a share component that specifies the Hydes Creek Water Source for more than 8 hours per day when the flow of water in Hydes Creek at the Hydes Creek at Kethels Road Bridge gauge is greater than 1 ML/day and less than or equal to 4 ML/day,
(f) subject to paragraph (g), water must not be taken under an access licence with a share component that specifies the Never Never Water Source for more than 8 hours per day when the flow of water in Never Never Creek at Promised Land Loop Road immediately upstream of the Arthur Keogh Reserve is greater than 2 ML/day and less than or equal to 9 ML/day,
(g) paragraphs (a)–(f) do not apply to the following:
(i) the taking of water under an access licence (excluding a local water utility access licence) to which Schedule 3 applies, for any purpose listed below, provided that the volume of water taken does not exceed 20 kilolitres per day per access licence or such lower amount specified in accordance with paragraph (h):
(A) fruit washing,
(B) cleaning of dairy plant and equipment for the purpose of hygiene,
(C) poultry watering and misting, or
(D) cleaning of enclosures used for intensive animal production for the purposes of hygiene,
(ii) the taking of water from a runoff harvesting dam or from an in-river dam pool,
(iii) the taking of water under all access licences that nominate a water supply work that may be used to take water from the alluvial sediments in these water sources to which the access rules for unregulated river access licences do not apply as specified in clause 65, and
(iv) the taking of water for the purposes of town water supply only under a local water utility access licence to which Schedule 3 applies, until such time as the Minister is satisfied that major augmentation of the access licence holder’s water supply system has occurred,
(h) the Minister may, in relation to an access licence to which paragraph (g) (i) applies, amend the licence to reduce the maximum daily volume limit, if the Minister is satisfied that the reduced volume is satisfactory to meet the purpose for the licence as referred to in paragraph (g) (i),
(i) the access rules specified in clauses 39A and 65 which apply to access licences that nominate a water supply work that may be used to take water from the alluvial sediments in these water sources as specified in those clauses,
(j) water must not be taken under an unregulated river (high flow) access licence or an unregulated river (subcategory “Aboriginal community development”) access licence when flows are in the Very Low Flow Class or A Class,
(k) water must not be taken from an in-river dam pool unless the in-river dam is passing such flows in such circumstances as specified on the water supply work approval for the in-river dam,
(l) the flows and circumstances to be specified on the water supply work approval for the in-river dam referred to in paragraph (k) are:
(i) the flows and circumstances that were specified in conditions on the Water Act 1912 entitlement that the approval replaces, or
(ii) where no flows and circumstances were specified on the Water Act 1912 entitlement, the flows and circumstances determined by the Minister.
Following the establishment or amendment of a flow class or flow classes within the Bellinger River Water Source, the Boggy Creek Water Source, the Coastal Bellinger Water Source, the Coastal Kalang Water Source, the Hydes Creek Water Source, the Never Never Creek Water Source and the Spicketts Creek Water Source under clause 18 (2) of this Plan, the Minister may under section 45 (1) (b) of the Act, amend subclauses (1), (2) and (3) to identify, establish and maintain planned environmental water in the relevant water source.
Subclause (3) does not apply to the taking of water under an access licence that is used only to account for the taking of water in association with an aquifer interference activity.
(Repealed)
This Part is made in accordance with sections 5 (3) and 20 (1) (b) of the Act.
Basic landholders rights exercised under section 52 of the Act must be exercised in accordance with any established by the Minister with respect to the reasonable use of water for domestic consumption and stock watering by landholders authorised to use water for either or both of those purposes.
The Minister may issue a direction under section 328 of the Act to restrict the exercise of basic landholder rights from these water sources.
Water from these water sources should not be consumed without prior treatment that is adequate to ensure its safety. Land use activities may have polluted the groundwater in some areas.
At the commencement of this Plan the water requirements of holders of domestic and stock rights within these water sources are estimated to total 3.6 megalitres per day (hereafter
(a) 0.4 ML/day in the Bellinger River Water Source,
(b) 0.1 ML/day in the Boggy Creek Water Source,
(c) 0.8 ML/day in the Coastal Bellinger Water Source,
(d) 0.6 ML/day in the Coastal Kalang Water Source,
(e) 0.1 ML/day in the Dalhousie Creek Water Source,
(f) 0.1 ML/day in the Hydes Creek Water Source,
(g) 0.5 ML/day in the Kalang River Water Source,
(h) 0.1 ML/day in the Never Never Creek Water Source,
(i) 0.1 ML/day in the Rosewood Creek Water Source,
(j) 0.1 ML/day in the Spicketts Creek Water Source, and
(k) 0.7 ML/day in the Thora–North Arm Bellinger River Water Source.
This Plan recognises that the exercise of domestic and stock rights may increase during the term of this Plan.
Increase in use of domestic and stock rights may occur as a result of an increase in the number of landholdings fronting rivers and lakes in these water sources and/or as a result of the increase in the exercise of basic landholder rights by existing landholders.
Increase in use of domestic and stock rights may also occur as a result of an increase in the number of landholdings overlying the alluvial groundwater through subdivision and/or as a result of the increase in the exercise of basic landholder rights by existing landholders.
The Minister may limit new domestic and stock rights in new subdivisions in any water source by regulation under section 52 (2) of the Act.
At the commencement of this Plan there are no native title rights in these water sources and therefore the water requirements for native title rights total 0 ML/year.
This Plan recognises that the exercise of native title rights may increase during the term of this Plan.
An increase in native title rights may occur as a result of the granting of native title rights under the Commonwealth’s Native Tile Act 1993.
The requirement for water under harvestable rights is the amount of water owners of land are entitled to capture pursuant to a harvestable rights order made under section 54 of the Act and published from time to time in the NSW Government Gazette.
This Part is made in accordance with section 20 (1) (e) of the Act.
This Plan establishes a bulk access regime for the extraction of water under access licences in these water sources having regard to:
(a) the environmental water provisions established under Part 4 of this Plan,
(b) the requirements for basic landholder rights identified under Part 5 of this Plan, and
(c) the requirements for water for extraction under access licences identified under Part 7 of this Plan.
The bulk access regime established in subclause (2):
(a) recognises the effect of climate variability on the availability of water as provided for under Part 3 of this Plan,
(b) establishes rules according to which access licences are granted as provided for in Part 8 of this Plan,
(c) recognises and is consistent with limits to the availability of water as provided for in Part 10, Division 1 of this Plan,
(d) establishes rules according to which available water determinations are to be made as provided for in Part 10, Division 1 of this Plan,
(e) establishes rules according to which access licences are managed as provided for in Parts 10 and 11 of this Plan, and
(f) establishes rules with respect to the priorities according to which access licences are to be adjusted as a consequence of any reduction in the availability of water as provided for in Part 10 of this Plan.
This Part is made in accordance with section 20 (1) (c) of the Act.
The amount of water specified in this Part represents the total volumes or unit shares specified in the share components on access licences in these water sources. The actual volumes of water available at any time will depend on climate, access licence priority and the rules in this Plan.
It is estimated that at the time of commencement of Part 2 of Chapter 3 of the Act, the share components of domestic and stock access licences authorised to extract water from these water sources will total 128 megalitres per year (hereafter
(a) 14 ML/year in the Bellinger River Water Source,
(b) 4 ML/year in the Boggy Creek Water Source,
(c) 2 ML/year in the Coastal Bellinger Water Source,
(d) 0 ML/year in the Coastal Kalang Water Source,
(e) 26 ML/year in the Dalhousie Creek Water Source,
(f) 1 ML/year in the Hydes Creek Water Source,
(g) 0 ML/year in the Kalang River Water Source,
(h) 15 ML/year in the Never Never Creek Water Source,
(i) 3 ML/year in the Rosewood Creek Water Source,
(j) 0 ML/year in the Spicketts Creek Water Source, and
(k) 63 ML/year in the Thora–North Arm Bellinger River Water Source.
It is estimated that at the time of commencement of Part 2 of Chapter 3 of the Act, the share components of local water utility access licences authorised to extract water from these water sources will total 1,613 ML/year, distributed as follows:
(a) 1,613 ML/year in the Bellinger River Water Source,
(b) 0 ML/year in all other water sources.
It is estimated that at the time of commencement of Part 2 of Chapter 3 of the Act, the share components of unregulated river access licences authorised to extract water from these water sources will total 2,993 unit shares, distributed as follows:
(a) 1,011 unit shares in the Bellinger River Water Source,
(b) 20 unit shares in the Boggy Creek Water Source,
(c) 90 unit shares in the Coastal Bellinger Water Source,
(d) 124 unit shares in the Coastal Kalang Water Source,
(e) 191 unit shares in the Dalhousie Creek Water Source,
(f) 429 unit shares in the Hydes Creek Water Source,
(g) 18 unit shares in the Kalang River Water Source,
(h) 723 unit shares in the Never Never Creek Water Source,
(i) 11 unit shares in the Rosewood Creek Water Source,
(j) 7 unit shares in the Spicketts Creek Water Source, and
(k) 369 unit shares in the Thora–North Arm Bellinger River Water Source.
It is estimated that at the time of commencement of Part 2 of Chapter 3 of the Act, the share components of unregulated river (high flow) access licences authorised to extract water from these water sources will total 0 unit shares, distributed as follows:
(a) 0 unit shares in the Never Never Water Source, and
(b) 0 unit shares in the Hydes Creek Water Source.
The water sources listed above are the only water sources within the Plan area which have been identified as suitable for unregulated river (high flow) access licences. This Plan allows for a specified amount of unregulated river access licences to be converted to unregulated river (high flow) access licences. However, at the commencement of this Plan, there are no existing access licences of this category, hence the 0 unit shares indicated.
It is estimated that at the time of commencement of Part 2 of Chapter 3 of the Act, the share components of aquifer access licences authorised to extract water from these water sources will total 228 unit shares, distributed as follows:
(a) 70 unit shares in the Bellinger River Water Source,
(b) 0 unit shares in the Boggy Creek Water Source,
(c) 19 unit shares in the Coastal Bellinger Water Source,
(d) 0 unit shares in the Coastal Kalang Water Source,
(e) 0 unit shares in the Dalhousie Creek Water Source,
(f) 120 unit shares in the Hydes Creek Water Source,
(g) 3 unit shares in the Kalang River Water Source,
(h) 6 unit shares in the Never Never Creek Water Source,
(i) 0 unit shares in the Rosewood Creek Water Source,
(j) 0 unit shares in the Spicketts Creek Water Source, and
(k) 10 unit shares in the Thora–North Arm Bellinger River Water Source.
The total share components for aquifer access licences specified in these water sources could be higher as a result of additional share components for unidentified aquifer access licences in the alluvial groundwater.
This Plan recognises that the total requirements for water for extraction within these water sources may change during the term of this Plan as a result of:
(a) the granting, surrender or cancellation of access licences,
(b) the granting, surrender or cancellation of access licences through a dealing under Part 12 of this Plan, and
(c) the variation of local water utility licences under section 66 of the Act.
The total share components identified in this Part may also change due to volumetric conversion of Water Act licenses that are currently non-volumetric.
This Part is made in accordance with sections 20 (2) (b), 61 and 63 of the Act, having regard to the limits to water availability in these water sources and the need to protect dependent ecosystems.
Applications for access licences may be made and access licences granted in these water sources, if the application is for:
(a) a specific purpose access licence for which application is provided for under clause 19 of the Water Management (General) Regulation 2004 (hereafter
the Regulation ) in accordance with section 61 (1) (a) of the Act,Note— At the commencement of this Plan, clause 19 of the Regulation provides for the following specific purpose access licences to be applied for:
(i) a local water utility access licence (subcategory “domestic and commercial”), for the purpose of domestic consumption and commercial activities,
(ii) a domestic and stock access licence (subcategory “domestic”), for the purpose of domestic consumption,
(iii) an unregulated river access licence (subcategory “town water supply”), for the purpose of supply to communities for domestic consumption and commercial activities,
(iv) an aquifer access licence (subcategory “town water supply”), for the purpose of supply to communities for domestic consumption and commercial activities, and
(v) any category of specific purpose access licence (subcategory “Aboriginal cultural”), for Aboriginal cultural purposes.
Note— Pursuant to sections 66 (3) and 66 (4) of the Act, the Minister may also vary a local water utility’s share component at 5 year intervals, or on application of the local water utility where there is rapid growth in population.
(b) an access licence with a zero share component in accordance with sections 61 (1) (b) and 63 (5) of the Act,
(c) an access licence that may be granted in accordance with a dealing that is permitted by Part 12 of this Plan,
Note— Dealings include the conversion of unregulated river access licences to unregulated river (high flow) access licences as specified in clause 74 of this Plan.
(d) any category of specific purpose access licence (subcategory “Aboriginal cultural”), for Aboriginal cultural purposes, up to 10 ML/year per application,
(e) an unregulated river access licence, or domestic and/or stock access licence in the Tidal Pool Management Zone where a history of extraction in the Tidal Pool Management Zone can be demonstrated prior to the 30 June 2006, and
(f) an unregulated river (subcategory “Aboriginal community development”) access licence, that can extract water from B Class flows only, has no more than minimal harm at the water source level impact assessment and provided no more than the following total unregulated river (subcategory “Aboriginal community development”) access licence share component has ever been issued or will cause the following total share component to be exceeded, in the respective water sources:
(i) 500 unit shares in the Bellinger River Water Source,
(ii) 91.5 unit shares in the Boggy Creek Water Source,
(iii) 500 unit shares in the Coastal Bellinger Water Source,
(iv) 500 unit shares in the Coastal Kalang Water Sources,
(v) 183 unit shares in the Hydes Creek Water Source, and
(vi) 146.4 unit shares in the Spicketts Creek Water Source.
Note— Approval for granting of an unregulated river (subcategory “Aboriginal community development”) access licence will be subject to assessment of the application in regard to the level of impact of the proposed extraction. This should include consideration of the potential impact on high flow (eg flows greater than the 50
th percentile flow) values, and any potential impact on the water source as a whole.Note— An unregulated river (subcategory “Aboriginal community development”) access licence is a specific purpose access licence and as such can only be the subject of limited trade that is consistent with the purpose for which the licence was granted. Aboriginal communities, enterprises and individuals are encouraged to seek financial assistance from funding bodies to purchase other categories of access licence if they require fully tradable licences.
Licences under subclause (2) (e) can only be granted to those water users previously exempted from requiring a Water Act 1912 entitlement.
In applying for a new access licence, the applicant must establish the purpose and circumstance relating to that access licence, and that the share component sought will be the minimum required to meet that purpose and circumstance.
Subclause (4) does not apply to a new access licence arising from:
(a) section 61 (1) (c), of the Act, where the right has been acquired by auction, tender or other open market process, or
(b) an access licence dealing, or
(c) subclause (2) (e).
Where total daily extraction limits have been established in a water source, any new access licence granted in the water sources, in accordance with this clause must have a share component within the respective total daily extraction limit initially assigned.
Where flow classes have not been established in a water source, any new access licence granted in the water sources, in accordance with subclause (2) (a) shall only be permitted to take water when flows exceed a level to be determined by the Minister and specified on the access licence.
This Part is made in accordance with sections 21 (b) and 21 (e) of the Act.
If the sum of the share components of access licences nominating a water supply work that is a runoff harvesting dam or an in-river dam is reduced via:
(a) a dealing,
(b) the surrender under section 77 (4) of the Act of an access licence and then the subsequent cancellation of an access licence under section 77A (6) of the Act,
(c) the amendment of the share component of the access licence by the Minister under section 68A, or
(d) the cancellation of an access licence under section 78 of the Act or via the compulsory acquisition of an access licence under section 79 of the Act,
the Minister may require the modification of the dam to ensure that the capability of the dam to capture water is reduced to reflect the reduction in share component.
Runoff harvesting dam and in-river dam are defined in the Dictionary.
(Repealed)
This clause is made in accordance with sections 21 (c) and 21 (e) of the Act, to minimise extraction interference between neighbouring bores and to ensure no more than minimal harm to groundwater sources and their dependent ecosystems.
Extracting groundwater results in the draw down of water levels in the vicinity of the extraction. It is important to manage these local effects. Extraction may result in unacceptable water level declines in other works/bore close by, increasing the pumping costs associated with this extraction, or even cutting off supply altogether. It may interfere with the results of the regional water level monitoring undertaken by the Department. It may also lower the water levels in groundwater dependent ecosystems and cultural features close by. Finally, it may mobilise contaminated groundwater in the area, drawing it towards to point of extraction. It is important, therefore, to manage the location at which groundwater is extracted to minimise these local impacts. This is achieved in this clause by applying minimum distance condition to works.
To minimise interference between water supply works in these water sources, the Minister must not grant an approval under section 95 of the Act or amend an approval under section 107 of the Act, where a water supply work being constructed or used to take water from the alluvial sediments in these water sources is proposed to be located within:
(a) 200 metres of a water supply work being constructed or used to take water from the alluvial sediments in these water sources nominated by another access licence,
(b) 200 metres of a water supply work being constructed or used to take water from the alluvial sediments in these water sources from which basic landholder rights is being extracted,
(c) 100 metres from the property boundary, unless negotiated with a neighbour for a lesser distance,
(d) 500 metres from a water supply work being constructed or used to take water from the alluvial sediments in these water sources from a local water utility or a major utility, and
(e) 100 metres from a Departmental observation or monitoring bore, unless a lesser distance is negotiated with the Department.
The distance restrictions in this clause apply to new or amended approvals. The distance restrictions also apply when a licence holder wants to nominate new or different works on an access licence.
The distance restrictions specified in subclause (2) does not apply where:
(a) the application relates to a work solely for the purpose of exercising basic landholder rights, or
(b) the application is for a replacement bore.
The distance restrictions specified in subclause (2) do not apply if:
(a) a hydrogeological study undertaken by the applicant, and assessed as adequate by the Minister, demonstrates minimal potential for adverse impacts on existing authorised extraction,
(b) all potentially affected access licence or approval holders have been notified by the proponent, and
Note— Potentially affected access licence holders are typically neighbouring access licence or approval holders and those in the near vicinity.
(c) there is a process for remediation in the event that any adverse impact occurs in the future, specified as conditions on the access licence.
Pursuant to section 45 (1) (b) of the Act, the Minister may add to or vary the distance restriction in subclause (2) to minimise the interference between authorised extraction after year 5 of this Plan or if the Minister identifies the need for further restrictions in a local impact area established under Division 4 of Part 11 of this Plan.
The Minister must not grant an approval under section 95 of the Act or amend an approval under section 107 of the Act, where a water supply work being constructed or used to take water from the alluvial sediments in these water sources is proposed to be located within:
(a) 100 metres of a contamination source as listed in Schedule 4, unless the proponent can demonstrate to the Minister’s satisfaction that a lesser distance will result in no more than minimal harm to the water source, and that extraction will not impact on the environment or cause a threat to public health as advised by the Minister for Health, or
(b) a greater distance than in paragraph (a) that the Minister nominates in order to ensure that no more than minimal harm will occur to the groundwater source, and that extraction will not impact on the environment or cause a threat to public health as advised by the Minister for Health.
Extraction of groundwater from a new water supply work being constructed or used to take water from the alluvial sediments in these water sources for any purpose between 100 metres and 500 metres of a contamination source as listed in Schedule 4, will require:
(a) an application to the Minister by the licence holder providing evidence that no drawdown of the groundwater within 100 metres of a contamination source will occur,
(b) the Minister to assess the application as adequate, and
(c) the Minister to approve the application.
Subclauses (6) and (7) may be applied by the Minister in relation to contamination sources not on Schedule 4, based on the results of a site inspection or other relevant information provided to the Minister.
Pursuant to section 45 (1) (b) of the Act, the Minister may vary Schedule 4 by inclusion or deletion of a contamination source based on the results of a site inspection or other relevant information provided to the Minister on that contamination source.
Unless the application is for a replacement water supply work that is part of a bore network for a local water utility or town water supply, the Minister must not grant a new approval under section 95, or an amended approval under section 107 in these water sources, if it would result in a water supply work being constructed or used to take water from the alluvial sediments in these water sources being authorised to extract water:
(a) for basic landholders rights only, within 100 metres of a high priority groundwater dependent ecosystem, excluding high priority karst environment groundwater dependent ecosystems, listed in and shown on the maps in Schedule 5, or
(b) from an access licence, within 200 metres of a high priority groundwater dependent ecosystem, excluding high priority karst environment groundwater dependent ecosystems, listed in and shown on the maps in Schedule 5, or
(c) within 500 metres of a high priority karst environment groundwater dependent ecosystem, listed in and shown on the maps in Schedule 5, or
(d) within 40 metres of the top of the high bank of any third order or above stream, or lagoon, or
(e) within 40 metres of any first and second order stream, unless the water supply work being constructed or used to take water from the alluvial sediments in these water sources is drilled into the underlying parent material, and the slotted intervals of the works commences deeper than 30 metres.
Subclause (10) will not apply to current authorised extraction from an existing water supply work which may be used to take water from the alluvial sediments in these water sources at current or equal share component.
The distance restrictions specified in subclause 10 (a) and (b) do not apply to the grant or amendment of a water supply work approval if the Minister is satisfied that no drawdown of water will occur at the perimeter of any groundwater dependent ecosystem listed in Schedule 5.
The distance restriction specified in subclause 10 (e) does not apply to the grant or amendment of a water supply work approval if the Minister is satisfied that a water supply work being constructed or used to take water from the alluvial sediments in these water sources will have minimal impact on base flows in the stream.
For the purpose of subclauses (11) and (12) the Minister may require the applicant to submit a hydrogeological study.
Subclause (10) (d) and (10) (e) does not apply to a new water supply work being constructed or used to take water from the alluvial sediments in these water sources required as part of a dealing involving the conversion of an unregulated river access licence to an aquifer access licence under section 71O of the Act and clause 74 of this Plan.
Pursuant to section 45 (1) (b) of the Act, the Minister may amend the exclusion distances in subclauses (10) based on the outcomes of further studies of groundwater ecosystem dependency undertaken or assessed by the Minister.
Pursuant to section 45 (1) (b) of the Act, the Minister may identify further high priority groundwater dependent ecosystems and include them in Schedule 5 after year 5 of the Plan, based on further studies of groundwater ecosystem dependency undertaken or assessed by the Minister.
Pursuant to section 45 (1) (b) of the Act, the Minister may identify that a high priority groundwater dependent ecosystem in Schedule 5 does not have groundwater dependency and delete it from Schedule 5, based on further studies of groundwater ecosystem dependency undertaken by the Minister.
The distance restrictions specified in subclauses (2), (6), (7) and (10) do not apply if the Minister is satisfied that the water supply work being constructed or used to take water from the alluvial sediments in these water sources is for monitoring or environmental management or remedial purposes.
The rules in this clause apply to water supply work approvals for water supply works that are authorised to take water from the alluvial sediments in these water sources.
Subject to subclauses (3) and (4), a water supply work that is located within a restricted distance specified in clause 39, must not, in any water year, be used to take more water than the volume of water that is equal to the sum of the share components of the access licences nominating that water supply work at the commencement of this Plan.
Subject to subclause (4), a water supply work that becomes located within a restricted distance specified in clause 39, as a result of an amendment to this Plan must not, in any water year, be used to take more water than the volume of water that is equal to the sum of share components of access licences nominating that water supply work at the date of the amendment.
Subclauses (2) and (3) do not apply:
(a) where a restricted distance does not apply in accordance with clause 39 (3) (a), (4), (6), (11), (12), or (17), or
(b) to the taking of water pursuant to basic landholder rights.
The Minister may specify a daily rate or annual volumetric limit for water taken by a water supply work that is located within a restricted distance specified in clause 39 pursuant to clause 39 (4), (6), (7), (11) and (12).
The daily rate or annual volumetric limit specified under subclause (5) will be as determined by the Minister to meet the relevant criteria specified in clauses 39 (4), (6), (7), (11) and (12).
The water quality from any bore can be affected by land use activities and inherent water quality in the aquifer. Water quality cannot be guaranteed and may be unsuitable for human consumption and other uses. The quality of water extracted should be tested before being used and appropriately treated. Such testing and treatment is the responsibility of the licence holder.
This Division is made in accordance with section 20 (2) (a) of the Act.
In accordance with clause 16 of this Plan, management of the long-term average annual extraction of water in these water sources will be undertaken in the context of the Bellinger River Catchment and Dalhousie Creek Catchment Extraction Management Units (hereafter
The long-term average annual extraction limit for each of these Units will be the total of:
(a) the quantity of water specified in conditions attached to or included in entitlements issued under Part 2 of the Water Act 1912 in the Unit, immediately prior to the commencement of Part 2 of Chapter 3 of the Act for the Unit, plus
(b) an estimate of annual extraction of water under domestic and stock rights and native title rights in the Unit at the commencement of this Plan, plus
(c) the sum of share components of access licences granted under clause 35 (2) (a), clause 35 (2) (e) and clause 35 (2) (f) in the Unit.
The long-term average annual extraction limit of these Units may be varied by the Minister if surface water dealings under Part 12 of this Plan result in issuing or cancellation of access licences in these Unit.
The long-term average annual extraction limit for the Bellinger River Catchment Extraction Management Unit may be varied upon the conversion of access licences from unregulated river access licence to an unregulated river (high flow) access licence.
The variation in subclause (2) will result in the long-term average annual extraction limit being reduced by the amount of the cancelled share component of the unregulated river access licence and increased by the amount of the share component of the granted unregulated river (high flow) access licence.
The total water extracted pursuant to basic landholder rights and access licences in these Units will be assessed each water year to determine if the long-term average annual extraction limit established by clause 42 for each extraction management unit has been exceeded.
A water year is defined in Schedule 1 as any 12 month period from 1 July.
Commencing in the fourth water year in which this Plan has effect, the assessment referred to in subclause (1) must compare the long-term average annual extraction limits established in clause 42 for the respective extraction management unit against the annual extraction averaged over the preceding three water years for that extraction management unit.
If the 3 year average of extraction in these Units exceeds the long-term average annual extraction limit established in clause 42 by 5% or greater, then the available water determination made for unregulated river access licences under clause 48 (1), for the following water year for unregulated river access licences in these water sources shall be reduced by an amount that is assessed as necessary by the Minister to return subsequent total water extraction in these Units to the long-term average annual extraction limit.
If the 3 year average of extraction in these Units is less than 95% of the long-term average annual extraction limit established in clause 42, the available water determination made under clause 48 (1) for the following water year for unregulated river access licences in these water sources shall be increased to such an extent as to allow total water extraction in these Units to increase to that extraction limit.
The effect of this subclause and clause 48 is that available water determinations for unregulated river access licences can never be greater than 1 ML per unit share, except for the available water determination made for the first year of the Plan.
Any reduction or increase to the available water determinations made under clause 48 (1) for unregulated river access licences in these water sources as a result of subclause (3) or (4) should be repeated for each of the subsequent two water years.
If the 3 year average of extraction in these Units exceeds the long-term average annual extraction limit established in clause 42 by 5% or greater, then the available water determination made for unregulated river (high flow) access licences under clause 49 (1), for the following water year for unregulated river (high flow) access licences in these water sources shall be reduced by an amount that is assessed as necessary by the Minister to return subsequent total water extraction in these Units to the long-term average annual extraction limit.
If the 3 year average of extraction in these Units is less than 95% of the long-term average annual extraction limit established in clause 42, the available water determination made under clause 49 (1) for the following water year for unregulated river (high flow) access licences in these water sources shall be increased to such an extent as to allow total water extraction in these Units to increase to that extraction limit.
The effect of this subclause and clause 49 is that available water determinations for unregulated river (high flow) access licences can never be greater than 1 ML per unit share, except for the available water determination made for the first year of the Plan.
Any reduction or increase to the available water determinations made under clause 49 (1) for unregulated river (high flow) access licences in these water sources as a result of subclause (6) or (7) should be repeated for each of the subsequent two water years.
If the 3 year average of extraction in these Units exceeds the long-term average annual extraction limit established in clause 42 by 5% or greater, then the available water determination made for aquifer access licences under clause 50 (1), for the following water year for aquifer access licences in these water sources shall be reduced by an amount that is assessed as necessary by the Minister to return subsequent total water extraction in these Units to the long-term average annual extraction limit.
If the 3 year average of extraction in these Units is less than 95% of the long-term average annual extraction limit established in clause 42, the available water determination made under clause 50 (1) for the following water year for aquifer access licences in these water sources shall be increased to such an extent as to allow total water extraction in these Units to increase to that extraction limit.
The effect of this subclause and clause 50 is that available water determinations for aquifer access licences can never be greater than 1 ML per unit share, except for the available water determination made for the first year of the Plan.
Any reduction or increase to the available water determinations made under clause 50 (1) for aquifer access licences in these water sources as a result of subclause (9) or (10) should be repeated for each of the subsequent two water years.
This Division is made in accordance with section 20 (2) (b) of the Act.
All available water determinations in these water sources shall be expressed as either:
(a) a percentage of the share component for all access licences where share components are specified as megalitres per year, or
(b) megalitres per unit share for all access licences where share components are specified as a number of unit shares.
An available water determination shall be made at the commencement of each water year for domestic and stock access licences in these water sources and shall provide an allocation of 100% of share components, except where the available water determination is made under subclause (2).
The available water determination made at the commencement of the first year of this Plan, for domestic and stock access licences in these water sources, shall provide an allocation of 200% of share components.
An available water determination shall be made at the commencement of each water year for local water utility access licences in these water sources and shall provide an allocation of 100% of share components, except where the available water determination is made under subclause (2).
The available water determination made at the commencement of the first year of this Plan, for local water utility access licences in these water sources, shall provide an allocation of 200% of share components.
An available water determination shall be made at the commencement of each water year for unregulated river access licences in these water sources and shall provide an allocation equal to 1 megalitre multiplied by the number of unit shares in the share component, or such lower amount as results from clauses 44 (3) or 44 (4), except where the available water determination is made under subclause (2).
The available water determination made at the commencement of the first year of this Plan, for unregulated river access licences in these water sources, shall provide an allocation equal to 2 megalitres multiplied by the number of unit shares in the share component.
The effect of this clause and clause 44 (4) is that available water determinations for unregulated river access licences can never be greater than 1 ML per unit share, except for the available water determination made for the first year of the Plan.
An available water determination shall be made at the commencement of each water year for unregulated river (high flow) access licences in these water sources and shall provide an allocation equal to 1 megalitre multiplied by the number of unit shares in the share component, or such lower amount as results from clauses 44 (6) or 44 (7), except where the available water determination is made under subclause (2).
The available water determination made at the commencement of the first year of this Plan, for unregulated river (high flow) access licences in these water sources, shall provide an allocation equal to 2 megalitres multiplied by the number of unit shares in the share component.
The effect of this clause and clause 44 (7) is that available water determinations for unregulated river (high flow) access licences can never be greater than 1 ML per unit share, except for the available water determination made for the first year of the Plan.
An available water determination shall be made at the commencement of each water year for aquifer access licences in these water sources and shall provide an allocation equal to 1 megalitre multiplied by the number of unit shares in the share component, or such lower amount as results from clauses 44 (9) or 44 (10), except where the available water determination is made under subclause (2).
The available water determination made at the commencement of the first year of this Plan, for aquifer access licences in these water sources, shall provide an allocation equal to 2 megalitres multiplied by the number of unit shares in the share component.
The effect of this clause and clause 44 (10) is that available water determinations for aquifer access licences can never be greater than 1 ML per unit share, except for the available water determination made for the first year of the Plan.
This Part is made in accordance with sections 20 (2) (b), 21 (a) and 21 (c) of the Act, having regard to:
(a) the environmental water rules established in Part 4 of this Plan,
(b) requirements for water to satisfy basic landholder rights identified in Part 5 of this Plan, and
(c) requirements for water for extraction under access licences in Part 7 of this Plan.
In accordance with section 85 of the Act, a water allocation account shall be established for each access licence in these water sources.
Water allocations will be accrued into each access licence water allocation account in accordance with the available water determinations made as specified in Division 2 Part 10 of this Plan.
Water allocations assigned from a water allocation account under Chapter 3 Part 2 Division 4 of the Act shall be debited from that water allocation account, and water allocations assigned to a water allocation account under Chapter 3 Part 2 Division 4 of the Act shall be credited to that water allocation account.
Water allocations may be assigned to, or from, these accounts by a water allocation assignment made under section 71T of the Act, where these are allowed under rules specified in Part 12 of this Plan.
Water allocations may also be recredited to access licence water allocation accounts under section 76 of the Act, in accordance with water return flow rules established under section 75 of the Act.
Section 341 of the Act makes it unlawful to take a volume of water under an access licence that exceeds the volume of water allocation, which is credited to the access licence at the time of water extraction.
The water allocation taken under an access licence in these water sources shall be the volume of water extracted by the approved water supply works nominated by the access licence, except where subclause (2) applies.
If water that, pursuant to an access licence, is committed as adaptive environmental water to be left in a river for environmental purposes, then the water allocation taken under that access licence shall be assumed to be 100% of the available water determination made in Division 2 Part 10 of this Plan.
The maximum volume that may be taken under or assigned from an access licence in these water sources at any time may not exceed the volume in the water allocation account.
For the period of any three consecutive water years after the first water year in which this Plan has effect, water taken under a domestic and stock access licence, a local water utility access licence, an unregulated river (high flow) access licence, an unregulated river access licence or an aquifer access licence in these water sources must not exceed a volume equal to the lesser of:
(a) the sum of:
(i) water allocations accrued to the water allocation account for the access licence from available water determinations in those three water years,
(ii) the water allocations carried over from the water year prior to those three water years under clause 57,
(iii) the net amount of any water allocations assigned to or from the water allocation account for the access licence under section 71T of the Act, in those three water years, and
(iv) any water allocations re-credited to the water allocation account for the access licence in accordance with section 76 of the Act, in those three water years, or
(b) the sum of:
(i) the share component of the access licence at the beginning of the first of those three water years,
(ii) the share component of the access licence at the beginning of the second of those three water years,
(iii) the share component of the access licence at the beginning of the third of those three water years,
(iv) the net amount of any water allocations assigned to or from the water allocation account for the access licence under section 71T of the Act, in those three water years, and
(v) any water allocations re-credited to the water allocation account for the access licence in accordance with section 76 of the Act, in those three water years.
For the period of the first three water years in which this Plan has effect, the maximum volume of water that may be taken under a domestic and stock access licence, local water utility access licence, unregulated river access licence, unregulated river (high flow) access licence or an aquifer access licence to which this clause applies must not exceed a volume equal to:
(a) 50% of the water allocations accrued to the water allocation account for the access licence from available water determinations in the first water year, plus
(b) the sum of water allocations accrued to the water allocation account for the access licence from available water determinations in the second and third water years, plus
(c) the net amount of any water allocations assigned to or from the water allocation account for the access licence under section 71T of the Act in those water years, plus
(d) any water allocations re-credited to the water allocation account for the access licence in accordance with section 76 of the Act in those water years.
The maximum water allocation that can be carried over in the accounts of domestic and stock, local water utility, unregulated river (high flow), unregulated river and aquifer access licences from one water year to the next shall be equal to:
(a) 100% of the access licence share component for access licences with share components expressed as ML per year, or
(b) 1 ML multiplied by the number of unit shares for access licences with share components expressed as a number of unit shares.
This Division is made in accordance with sections 20 (2) (b) and 21 (a) of the Act.
At the commencement of this Plan, total daily extraction limits (hereafter
No TDELs will be initially assigned to any category of access licence in these water sources.
There are no unassigned TDELs in these water sources.
At the commencement of this Plan, there are no individual daily extraction limits established for licence holders (hereafter
There are no unassigned TDELs in these water sources.
(Repealed)
The Minister may, under section 45 (1) (b) of the Act, add a licence to Schedule 3 following written request by the holder of an access licence, but only if extraction under the licence is for the purposes established in clause 21 (3) (g) (i), and the purpose was on the entitlement that was replaced by the access licence.
The Minister may under section 45 (1) (b) of the Act remove a licence from Schedule 3 if:
(a) any access licence dealing results in the water being extracted under that licence from a different location,
(b) an alternative water supply is obtained, that satisfies the requirements of clause 21 (3) (g) (i), or
(c) the licence is surrendered or cancelled or the purpose ceases to exist.
Following an assessment of the continuing requirements for access under this clause the Minister may, under section 45 (1) (b) of the Act amend or delete Schedule 3, if such a review determines that access under this clause is no longer required.
The Minister may add an access licence or a Water Act 1912 entitlement to Schedule 3 if the Minister is satisfied that the water supply system used to take, store and deliver water has not undergone major augmentation since the commencement of this Plan.
The Minister may remove an access licence or Water Act 1912 entitlement from Schedule 3 if the Minister is satisfied that the water supply system used to take, store and deliver water has undergone major augmentation since the commencement of this Plan.
When undertaking this review the Water and Energy Commission is required to call for public submissions. The Commission will take into consideration any submission received as well as any other relevant State-wide or regional government policies or agreements that apply to the Local Land Services region.
In accordance with section 44 of the Act, this Plan will be audited at intervals of no more than five years, for the purpose of ascertaining whether its provisions are being given effect to. This audit is to be carried out by an audit panel appointed by the Minister in consultation with the water management committee, where one exists.
Implementation Program
In accordance with section 51 of the Act, the Minister may establish an Implementation Program that sets out the means by which the provisions of this Plan are to be achieved.
It is proposed that the Minister establish an Implementation Program for this Plan. Pursuant to section 51 (5) of the Act, the Implementation Program is to be reviewed annually by the Minister to determine whether it is effective in implementing this Plan.
The results of the review of the Implementation Program are included in the annual report for the Department.
Amendments specified throughout this Plan, and in this Part, are amendments authorised by this Plan.
Amendments authorised by this Plan are taken to include any consequential amendments required to be made to this Plan to give effect to that particular amendment.
For example, if Part 1 is amended to add a new management zone, this may require amendment to other parts of this Plan to include rules for that management zone.
An amendment authorised by this Plan which results in a variation of the bulk access regime, is an amendment authorised by this Plan for the purposes of sections 87 (2) (c) and 87AA of the Act.
This Plan may be amended so as to provide for the floodplain harvesting of water, subject to the amendments not affecting the outcomes of the long-term average annual extraction limit specified within this Plan.
This means that this Plan can be changed to issue and manage floodplain harvesting licences provided that the long-term average annual extraction limit (LTAAEL) does not increase or decrease. Floodplain harvesting in coastal systems is limited compared to inland systems. By not amending the LTAAEL with the granting of these licences, coastal systems are being consistent with inland systems where growth is managed within the existing LTAAEL.
The Minister may, under section 45 (1) (b) of the Act amend this Plan, where required, to include provisions and rules for the waters in the coastal sands that are within and outside the area of this Plan.
Coastal sands are defined as the sand plains and sand dunes associated with beach complexes.
The Minister may, under section 45 (1) (b) of the Act amend this Plan, where required, to include provisions and rules for the alluvial aquifer that is downstream of the tidal limit and within or outside of the area of this Plan.
The Minister may, under section 45 (1) (b) of the Act, amend:
(a) Part 3,
(b) Part 4,
(c) Part 8,
(d) Part 9,
(e) Part 10,
(e) Part 11, Division 2 and 3,
(f) Part 12, and
(h) Part 13,
to include rules for any new category of access licence established under the Act for the purpose of stormwater harvesting.
This Plan may also be amended in accordance with the following clauses:
(a) clause 5 (4) in respect to amending an existing, or establishing a new or additional management zones,
(b) clauses 17 (2), 17 (3) and 17 (4) in respect to additional or amendment to flow reference points,
(c) clause 18 (2) in respect to the establishment of new or additional flow class or classes,
(d) clause 21 (4) in respect to the identification, establishment and maintenance of planned environmental water,
(e) clause 39 (5) in respect to the distance restrictions to minimise interference between extraction,
(f) clause 39 (9) in respect to contamination sources,
(g) clauses 39 (11), 39 (14), 39 (15) and 39 (16) in respect to high priority groundwater dependent ecosystems,
(h) Part 11 with respect to:
(i) amending rules in relation to record keeping including amendments in relation to requirements for Logbooks, or
(ii) specify different standards or requirements for decommissioning water supply works or construction requirements for water supply works in clauses 80 and 80A, and
(i) this Plan may be amended to allow for the management of aquifer interference activities.
The following definitions apply to this Plan in addition to the definitions set out in the Act:
Natural drawdown may occur due to seasonal climatic changes. Groundwater pumping may also result in seasonal and long-term drawdown.
(a) Very Low Flows may be a class on their own,
(b) low flows may be categorised as A Class flows,
(c) moderate flows may be categorised as B Class flows, and
(d) high flows may be categorised as C Class flows.
The Strahler system is explained as follows:
• Starting at the top of a catchment, any watercourse that has no other watercourses flowing into it is classed as a 1st order watercourse,
• Where two 1st order watercourses join, the watercourse becomes a 2nd order watercourse,
• If a 2nd order watercourse is joined by a 1st order watercourse—it remains a 2nd order watercourse,
• When two or more 2nd order watercourses join they form a 3rd order watercourse,
• A 3rd order watercourse does not become a 4th order watercourse until it is joined by another 3rd order watercourse and so on.
Levels of assessed contribution:
• FULL—contributes to target in full
• HIGH—while not fully contributing to target is considered a good level of contribution
• PARTIAL—goes some way to contributing to the target
• LOW—only small degree of contribution to the target
Relevant Target | Level of contribution | Comments |
Target 1c Long-term average annual extraction limits which are ecologically sustainable, and which minimise downstream impacts, established in all coastal water sources. | FULL | An overall long-term average annual extraction limit has been set for each extraction management unit. The unlicensed extraction downstream of the current limit for licensing under the Water Act 1912 will be incorporated into that long-term average annual extraction limit once volumetric conversion occurs. |
Target 1f Rules for adjustments to future available water determinations in the event that the extraction limits are exceeded, clearly prescribed in consultation with the relevant management committee, and acted upon. | FULL | Rules for Available Water Determination (AWD) adjustment are set out in Part 10 of this Plan and ensure that the long-term average annual extraction limit is not exceeded. This Plan is a Minister’s plan and therefore no management committee involvement required. |
Target 2 All management plans incorporating mechanisms to protect and restore aquatic habitats, and the diversity and abundance of native animals and plants, with particular reference to threatened species, populations and communities and key threatening processes. | HIGH | Cease to pump rules protect and restore aquatic habitats. These rules were based on risk to instream values. These values were based on: naturalness; diversity; rarity including threatened species, populations and communities; and special features. Trading rules were designed to reduce stress in water sources with high instream values. |
Target 4a Wherever the frequency of “end of system” daily flows would be less than 60% of the pre-development level without environmental water rules or extraction limits, the flows increased to 60% of pre-development levels or increased by at least 10% of the pre-development frequency. | PARTIAL | Access rules and trading rules will contribute to restoration of flow in proportion to the risk to instream values. High risk water sources will have a higher proportion and low risk a lower proportion. |
Target 4b Frequency of “end of system” daily very low flows (as defined by local field investigation) protected or restored to pre-development levels to maintain or restore their critical ecological functions, drought refuges and habitat connectivity. In the absence of such local assessments, protection extended up to at least the pre-development 95 | HIGH | Cease to pump level at end of system established for all water sources to protect daily very low flows, excluding Dalhousie Creek Water Source and Spicketts Creek Water Source. |
Target 5 Access rights for water access licensees clearly and legally specified in terms of share and extraction components. | FULL | The Plan specifies access rights in terms of share and extraction components. |
Target 6b For surface water sources, a pathway for reducing the share components to 200 percent of the long term average annual extraction limit to be established not later than the end of the term of the SWMOP. | FULL | Long-term average annual extraction limit based on existing entitlement plus exemptions. No pathway required |
Target 7 Mechanisms in place to enable Aboriginal communities to gain an increased share of the benefits of the water economy. | HIGH | The Plan provides for the granting of access licences for Aboriginal commercial purposes available in low hydrological stressed, and medium to low instream value, water sources. The Plan also provides market opportunities for Aboriginal Water Trust. |
Target 8 Daily extraction components specified and tradeable, subject to metering, reporting and compliance, for at least 50 percent of unregulated river access licences and for 80 percent of stressed unregulated rivers. | PARTIAL | Flow classes established but no daily extraction limits set. |
Target 10 Degree of connectivity between aquifers and rivers assessed, and zones of high connectivity mapped to enable base flows to the river to be maintained or improved. | HIGH | Interaction between rivers and groundwater considered in developing the Plan. Rules for works in close proximity to river in adjacent Groundwater Plans consistent with the Plan. |
Target 12 Measures in place in all water sources subject to a gazetted water sharing plan to protect domestic and stock rights from the impact of other water access and use. | FULL | The Plan recognises domestic and stock rights and provides access rules to protect the impact. Cease to pump access rules will protect basic landholder rights users from the impact of extraction by access licences. |
Target 13 The knowledge sharing, training and resources necessary to ensure that Aboriginal people have the capacity to be effectively involved in water management identified and addressed | PARTIAL | Liaison with regional Aboriginal networks and work undertaken with Aboriginal staff to identify appropriate communication mechanisms and approaches for local Aboriginal Land Councils to provide input to the planning process. Given limited information on specific cultural values Plan adopts an approach to protect cultural values through general environmental protection provided by rules. Aboriginal dependence on water recognised through Basic Landholder Rights and specific access licences for cultural and commercial purposes. |
Target 14 Water sources, ecosystems and sites of cultural or traditional importance to Aboriginal people identified, plans of management prepared, and measures put in place to protect and improve them. | LOW | Where possible, water sources, ecosystems and sites of cultural or traditional importance to Aboriginal people were identified and the risks from water extraction assessed in the preparation of the Plan. Further comment from Aboriginal communities is being sought during the exhibition of the draft plan. Access and dealing rules established to protect and enhance. |
Target 16a All share components of access licences tradeable. | HIGH | Part 12 of the Plan provides for trading of access licence share components. |
Target 16c Conversion factors and protocols established to facilitate trading and dealings between water sources, whilst also protecting existing access and environmental water. | FULL | Part 12 of the Plan establishes the protocols for trading between water sources. An exchange rate of 1:1 for trading between water sources within each extraction management unit has been adopted, and a conversion factor of 2.5:1 for high flow access in the Hydes Creek and Never Never Water Sources. |
Target 16e Any unassigned access rights identified and clear mechanisms established for their future assignment. | FULL | The Plan has identified that there is no unassigned access rights. The Plan identified which access licence categories can be granted and the rules for variation to the LTAEL as a result of granting those access licences. |
Target 16f Zones established where necessary for environmental protection and limits/constraints on water dealings in them made explicit. | HIGH | The Plan establishes management zones in Part 1 of the Plan and establishes flow rules for specific management zones in clause 18 of the Plan, and the trading rules within and between zones in Part 12 of the Plan. |
Target 35 All management plans incorporating water quality objectives that have considered Government approved Interim Environmental Objectives, the current Australian and New Zealand Environment and Conservation Council Guidelines and the recommendations of relevant Healthy Rivers Commission Inquiries. | PARTIAL | The Plan contain a water quality objective for the contribution to the maintenance of water quality. There are no recommendations from any Healthy Rivers Commission Inquiries over the area of the Plan. |
Schedule 3 currently lists Water Act 1912 entitlements from which Water Management Act 2000 access licences will be derived upon commencement of this Plan.
30SL040955
30SL065242
30SL065813
30SL066237
30SL039469
30BL184010
30BL130392
30BL130393
30BL130394
30BL142251
Contamination sources in the Bellinger River Area Unregulated and Alluvial Water Sources include:
(a) on site sewage disposal systems or septic tanks,
(b) any significantly contaminated land within the meaning of the Contaminated Land Management Act 1997,
(c) any sites with an historical use listed in Table 1 of Managing Land Contamination. Planning Guidelines. SEPP 55—Remediation of Land, and
(d) any relevant sites listed in an agency database relating to contamination sources.
The contamination sources listed in this Schedule may change during the period of this Plan. The Offices of the Department of Water and Energy, shown in Appendix 2, should be contacted for a current list.
At the commencement of this Plan, no high priority groundwater dependent ecosystems or high priority karst environment groundwater dependent ecosystems have been identified in this Schedule.
High priority groundwater dependent ecosystems are currently under investigation and some of these may be identified during the term of this Plan. The full list of potential GDEs will be identified on the DWE GDE Register and as a precautionary approach, will be considered by staff in the assessment of any works approval within the plan area. If verified as high priority groundwater dependent ecosystems, the Schedule will be amended to include further GDEs.
Water Source | Beneficial Uses |
Bellinger River | Irrigation and ecosystem protection |
Boggy Creek | Irrigation and ecosystem protection |
Coastal Bellinger | Irrigation and ecosystem protection |
Coastal Kalang | Irrigation and ecosystem protection |
Dalhousie Creek | Irrigation and ecosystem protection |
Hydes Creek | Irrigation and ecosystem protection |
Kalang River | Irrigation and ecosystem protection |
Never Never | Irrigation and ecosystem protection |
Rosewood Creek | Irrigation and ecosystem protection |
Spicketts Creek | Irrigation and ecosystem protection |
Thora–North Arm Bellinger River | Irrigation and ecosystem protection |
Copies of the Plan Map may be inspected at the following offices:
• NSW Office of Water
Department of Trade and Investment, Regional Infrastructure and Services
10 Valentine Ave
PARRAMATTA NSW 2150
• NSW Office of Water
Department of Trade and Investment, Regional Infrastructure and Services
Level 3, 49 Victoria St
Grafton, NSW 2460
• NSW Office of Water
Department of Trade and Investment, Regional Infrastructure and Services
The Harrington Building
Level 1, 41 Belgrave Street
KEMPSEY NSW 2440
• NSW Office of Water
Department of Trade and Investment, Regional Infrastructure and Services
AMP Centre
24 Gordon Street
Any notifications that may be required to be made to the Minister, as specified in this Plan can be addressed to the following office:
• NSW Office of Water
Department of Trade and Investment, Regional Infrastructure and Services
Locked Bag 10
Grafton, NSW 2460
0
0
0