Plan Change 7 and Plan Change 2 - What you need to know
Environment Canterbury has notified Plan Change 7 to the Canterbury Land & Water Regional Plan (CLWRP) and Plan Change 2 to the Waimakariri River Regional Plan for public submissions. Read the overview presentation (PDF File, 5.09MB) and the information below to find out more about what this might mean for you.
Council publicly notified two proposed plan changes for public submissions:
Plan Change (PC) 7 is a proposed plan change to the Canterbury Land & Water Regional Plan (CLWRP).
The LWRP sets out the planning framework for the management of land and water resources in Canterbury.
It is one of the key methods for implementing the Canterbury Water Management Strategy, a community-led collaborative approach to improve freshwater outcomes throughout the region.
PC7 is split into three parts (Parts A, B and C).
Part A is an ‘Omnibus’ change proposing amendments to region-wide provisions (policies, rules, maps and schedules).
Part A aims to:
- Improve freshwater outcomes for Canterbury
- Protect habitats of indigenous freshwater species
- Enable consideration of Ngāi Tahu values in relation to a broader range of activities
- Provide the use of managed aquifer recharge (a technique to improve the volume and quality of groundwater) across the region
- Establish a new nutrient framework for commercial vegetable growing operations
- Implement recommendations from the Hinds Drains Working Party.
Parts B and C
Parts B and C of PC7 relate to the Orari Temuka Opihi Pareora (OTOP) and Waimakariri sub-regions respectively.
These parts have been developed in collaboration with the Waimakariri and OTOP Zone Committees, and implement recommendations in the Zone Implementation Programme Addenda (ZIPAs).
Key changes introduced by Parts B and C include:
- New water quality limits for groundwater and surface water
- Requirements for farms to further reduce nitrogen losses over time
- Increases to minimum flows for rivers and streams
- A cap on the volume of water available for allocation
- Requirements to exclude stock from a broader range of waterbodies.
Plan Change 2 (PC2) is a proposed plan change to the Waimakariri River Regional Plan (WRRP). The WRRP promotes sustainable management of surface water and hydraulically connected groundwater within the Waimakariri catchment.
PC2 is the first step in a move to bring all rules relating to the Waimakariri sub-region into a single planning document – the Land & Water Regional Plan (LWRP). The WRRP would continue to apply to activities within the main stem of the Waimakariri River, its upper catchment, and tributaries south of the mainstem.
Activities in the rest of the Waimakariri sub-region would instead be managed by the LWRP (including provisions in section 8 which apply specifically to the Waimakariri sub-region).
No. Once the ZIPAs have been accepted by Council they are final – this happened last December. There is now the opportunity to have your say on the content of the proposed plan changes through a public submission process.
How to make a submission on proposed Plan Change 7
Submissions can be made by:
- email to email@example.com with “Plan Change 7 to the LWRP Submission” in the subject line - Please use this form for your submission (PDF File, 453.99KB)
- post to PO Box 345, Christchurch 8140 - Please use this form for your submission (PDF File, 453.99KB)
- Or via the ePlan portal
The period for submissions on Proposed Plan Change 7 to the LWRP closes on 13 September 2019.
How to make a submission on proposed Plan Change 2
Submissions can be made by :
- email to firstname.lastname@example.org with “Plan Change 2 to the WRRP Submission” in the subject line - Please use this form for your submission (PDF File, 454.86KB)
- post to PO Box 345, Christchurch 8140 - Please use this form for your submission (PDF File, 454.86KB)
- via the ePlan portal
The period for submissions on Proposed Plan Change 2 to the WRRP closes on 13 September 2019
The submission period will close on 13 September 2019. Following the close of submissions (including further submissions), a public hearing of submissions and evidence will happen.
The hearing in front of an independent hearing panel is likely to be held during the first half of 2020.
The independent hearing panel will prepare a set of recommendations for Council to consider and potentially adopt as its decision.
The rules in both plan changes are now legally effective. However, new activities and those established before notification of the proposed plan changes (20 July 2019) are treated differently.
- New activities must comply with rules in both the relevant operative plan and in the proposed plan changes.
- If an activity cannot meet the requirements of a ‘permitted activity’ rule in both the operative plan and proposed plan changes, a resource consent will be required.
- An existing activity is one that was established before notification of the proposed plan changes on 20 July 2019.
- Where an existing activity is permitted under the operative plan, but requires a resource consent under rules in the proposed plan changes, the activity may continue without a resource consent up until 6 months after the plan change becomes operative. Certain criteria apply, including that the activity was lawfully established and there is no change in its scale, intensity or character.
Plan Change 7 is in 3 parts:
The Land & Water Regional Plan (LWRP) has been operative for 7 years and there have been changes in that time which now need to be taken into account across the region.
Changes are proposed to make sure the LWRP responds to new directives from central government, emerging environmental issues, and changes in matters that are strategic priorities for Environment Canterbury.
Proposed changes to policies, rules and schedules cover the following key topic areas:
- National Policy Statement for Freshwater Management
- National Environmental Standards for Plantation Forestry
- Ngāi Tahu outcomes
- Habitats of indigenous freshwater species
- Fish passage
- Freshwater bathing
- Commercial vegetable growing operations
- Hinds Drains Working Party recommendations
- Managed aquifer recharge
Part A introduces a new cultural outcome for lakes and rivers in Canterbury, with the objective that freshwater mahinga kai is abundant and safe to gather.This outcome is delivered partly through new policies and rules which place restrictions on activities that that could reduce the quantity or quality of freshwater.
In addition, Part A of PC7 proposes to change 23 rules to enable decisionmakers to consider the potential effects of activities on Ngāi Tahu values and customary activities. Changes are also proposed to templates for Farm Environment Plans (Schedule 7) and Farm Management Plans (Schedule 7A).
The proposed changes would require farmers to identify all waipuna (springs) on their farm, and describe the actions they will implement to minimise effects on water quality.
The LWRP includes Schedule 17 which lists significant salmon spawning sites in Canterbury.
Part A of PC7 proposes to add 32 additional salmon spawning sites into Schedule 17, 22 of which are new sites located throughout Canterbury.
An additional nine sites that are currently listed in the Waimakariri River Regional Plan are proposed to be transferred to the LWRP.
The inclusion of these additional sites would mean additional restrictions applied to activities that could damage spawning sites. Restrictions include prohibiting access by farmed cattle, deer and pigs into salmon spawning sites.
Habitats of 11 indigenous freshwater species (including native fish, mussels and crayfish) have been identified and will be included on the LWRP planning maps.
New policies require damage to indigenous habitats to be avoided, except where the adverse impacts can be offset through the creation of new habitats. Proposed changes restrict the types of activities that may occur as a permitted activity within a mapped habitat area.
Activities with the potential to cause direct damage to habitats (such as vegetation clearance and earthworks) or indirect damage (abstraction of water, for example), must obtain a resource consent and the effects of the proposal on the habitat will be considered and assessed.
New policies direct that safe passage of indigenous fish through instream structures and barriers is to be provided for. New in-stream structures are to be appropriately designed and constructed to enable safe fish passage, and users are encouraged to modify or remove existing barriers to fish passage.
Resource consents would be required for activities that occur within, or adjacent to, mapped indigenous freshwater habitat areas.
In addition, activities which significantly compromise the values of a habitat (such as farmed cattle, deer or pigs in a habitat) would be prohibited.
Changes to provide for safe fish passage would not increase the number of resource consents required. However, if the installation of a structure in a river or lake requires a resource consent, there would be an expectation that the structure is designed and constructed to enable fish passage.
What changes are proposed?
PC7 proposes to add an additional 64 freshwater bathing sites into Schedule 6 of the LWRP. Farmed cattle, deer and pigs would need to be excluded from waterbodies upstream of any freshwater bathing site listed in Schedule 6.
How were the freshwater bathing sites identified?
A combination of information sources were used to identify the new freshwater bathing sites. Sites included in Schedule 6 include those identified in the ‘River Values Assessment System’ report as having high recreational values, sites monitored as part of Environment Canterbury’s recreational water quality monitoring programme, and sites identified by zone committees as popular freshwater bathing sites.
Why do farmed cattle, deer and pigs need to be excluded from freshwater bathing sites? What are the associated costs of doing this?
Livestock can contribute to degraded water quality through increased sedimentation (from pugging and damage of the bed and banks), and can increase the risk of pathogens entering waterways.
The costs of excluding stock from waterways would depend on the topography of the location, and the method used to exclude the stock (such as full fence, hot-wire or alternative method).
Unlike traditional farming enterprises such as dairy, sheep and beef operations, commercial vegetable growers frequently need to relocate their crops to new locations to prevent crop disease. Growers typically achieve this by rotating crops through a combination of permanently owned land and short-term lease.
The LWRP include rules to manage the impacts of farming activities (including commercial vegetable growing operations) on the environment. These rules include property-based nitrogen limits which restrict how much nitrogen may be leached from a property. The current rules allocate nitrogen based on land use from 2009 to 2013. The current framework poses two problems for growers:
- Nitrogen loss rates for the 2009 – 2013 period may not be available if the land is no longer part of the commercial growing operation (for example, if the land was subject to a short-term lease).
- New land available for lease often does not have a high enough nitrogen ‘baseline’ to accommodate ongoing operations.
Part A of PC7 proposes a new framework to manage nutrient losses from commercial vegetable growing operations. All commercial vegetable growing operators must obtain a land use consent for their activity, prepare and implement a Farm Environment Plan, and have that plan regularly audited.
Commercial vegetable growing operators must restrict the area of land used for the growing operation to an area that is no larger than that used during the 2009 – 2013 period. Growers must also demonstrate how they will achieve any nitrogen loss reductions required by a sub-region section of the plan.
Expansions of existing commercial vegetable growing operations, or the establishment of a new commercial vegetable growing operations may occur, but only if the grower can comply with nitrogen limits that apply to land at a new location.
If land that is used, or intended to be used, for commercial vegetable growing operations is located in a different sub-region or Nutrient Allocation Zone, growers have two options when applying for resource consent.
They could choose to lodge separate applications for each sub-region or Nutrient Allocation Zone that they grow in, or they could lodge one application for an operation that spans multiple sub-regions or Nutrient Allocation Zones.
The first option means only matters listed in Rule 5.42CB would be considered when a proposal is assessed, while under the second option a wider range of effects of the proposal may be considered.
Managed Aquifer Recharge (MAR) systems allow high-quality clean water to infiltrate the ground to recharge groundwater and hydraulically connected surface waterbodies.
MAR systems are typically used to recharge aquifers subject to declining yields, address saltwater intrusion, or sustain/improve the functioning of ecosystems and the quality of groundwater.
A MAR system has recently been trialled in Canterbury in Hinds/Hekeao using water sourced from the Rangitata River. The results to date have shown improvements in the quality of localised groundwater. A further 16 trial sites have been consented in the Mayfield-Hinds and Valetta catchments and a further two sites in the Waimakariri District.
MAR systems involve large quantities of water being abstracted from surface water and discharged into groundwater. Oversight of these systems (by way of a resource consent) is required to ensure the potential adverse effect of these activities can be considered and managed.
Part A responds to recommendations made by the Hinds Drains Working Party to the Ashburton Zone Committee. These recommendations were not available before the notification of Plan Change 2 to the LWRP (Hinds / Hekeao Plains Area).
The new provisions provide a more enabling framework for consent holders to substitute their existing surface water or stream depleting groundwater consents for deeper groundwater. This approach will enable a reduction in over-allocation in lowland streams.
The Hinds Drains Working Party and the Ashburton Zone Committee recommended retaining the current minimum flow sites on the basis that managed aquifer recharge and targeted stream augmentation will probably have an influence on waterways. Those impacts need to be clearly established before minimum flow limits are set.
With new water quality limits for drinking water supplies that are consistent with the NZ Drinking Water Standards. In addition, Part B includes methods to maintain current good water quality, and improve degraded water quality over time.
The freshwater outcomes for the OTOP sub-region are set to maintain existing good water quality, or improve water quality where it is currently degraded. Improved water quality will mean that some rivers will meet national standards for swimmable contact recreation and improved habitat to encourage and enable mahinga kai gathering.
New polices are proposed to provide protection to wāhi tapu, wāhi taonga, nohoanga, waipuna and tuhituhi neherā.
In addition, a ‘Mātaitai Protection Zone’ and a ‘Rock Art Management Area’ have been identified and new restrictions imposed on activities within these zones/areas.
Farmers in these zones would need to obtain a land use consent for their farming activity, prepare and implement a Farm Environment Plan, and have that plan regularly audited.
New environmental flow and allocation regimes have been proposed for parts of the OTOP sub-region. Higher minimum are proposed to be introduced over time, which would ensure more water is retained in the river to provide for ecosystem values.
An increase to minimum flows would reduce the reliability of water for abstractors. However, the introduction of new minimum flows have been staged, allowing time for irrigators and industry to adapt to proposed changes.
The provisions in Part B of PC7 substantially implement the recommendations in the OTOP Zone Committee’s ZIPA. Key differences between recommendations in the ZIPA and Part B of the plan change include:
- The introduction of the ‘Mātaitai Protection Zone’ and ‘Rock Art Management Areas’. These areas had not been mapped at the time the ZIPA was prepared and have subsequently been introduced, together with additional restrictions on activities in these zones.
- A revised management regime for management of surface water flows downstream of the Opuha Dam has been developed since the ZIPA was finalised. The framework aligns with the principles included in the ZIPA.
The OTOP sub-region has one of the highest densities of rock art sites in New Zealand. These sites are taonga (treasured/sacred) to Te Rūnanga o Arowhenua and Te Rūnanga o Waihao who actively contribute to their conservation and management.
Rock art is typically found on limestone outcrops and some activities (such as irrigation, discharges and land uses) can cause damage to rock art if not appropriately managed. Part B of PC7 would require farming activities with irrigation in the Rock Art Management Areas to obtain a resource consent. This process allows the potential effects of a farming activity to be assessed on a case-by-case basis.
A Mātaitai Protection Zone is proposed, together with new restrictions on farming activities, to protect the quality of water around the mātaitai (customary fishing area). New rules require a resource consent and audited Farm Environment Plan for any farm in the zone that directly adjoins a surface waterbody and which carries out irrigation or winter grazing of cattle.
The Mātaitai Protection Zone also contains a predominance of waipuna (springs) which are taonga (treasured/sacred) to Ngāi Tahu. Waipuna are vulnerable to pollution, damage or destruction from a variety of activities. Protecting waipuna in the OTOP sub-region by including new restrictions on farming activities is important for protecting biodiversity and mahinga kai values.
Technical investigations have shown that freshwater quality across the sub-region generally meets water quality limits in the National Policy Statement for Freshwater Management (NPFSM) and the Drinking Water Standards for New Zealand. However, there are localised areas where elevated concentrations of nitrate-nitrogen have been detected in groundwater (referred to as ‘High Nitrogen Concentration Areas’).
Within these areas, farming activities would be required to further reduce their nitrogen losses over time. Reductions of 10% (for dairy) and 5% (for other farming activities) would be required by 2030, with a further 10% and 5% respectively by 2035.
Yes. More farms would require a resource consent under proposed PC7. Irrigated farms within a Rock Art Management Area would be required to obtain a resource consent, as would farms in the Mātaitai Protection Zone with any irrigation or winter grazing of cattle or deer.
The Orari and Pareora Freshwater Management Units (FMUs) have recently been subject to plan changes that introduced revised surface water and allocation regimes. No significant changes to the allocation framework are proposed.
Within the Temuka and Opihi FMU, new environmental flow and allocation regimes are proposed, with stepped increases in minimum flows over time.
It is anticipated new the inclusion of higher minimum flows for rivers and additional restrictions on farming activities may help reduce algal blooms in rivers.
OEFRAG would still provide advice to Environment Canterbury on water shortage directions sought under section 329 of the Resource Management Act. Water shortage directions may be issued when there is a serious temporary shortage of water.
Yes. To date water shortage directions have been sought regularly and on a pre-emptive basis to prevent potential water shortages during the irrigation season.
The flow and allocation regime and minimum lake levels in the Opihi River Regional Plan (ORRP) are not appropriate if the community’s aspirations for the Opihi River are to be met. The proposed flow and allocation framework introduced by Part B of PC7 is considered a more effective method for managing releases of water from the Opuha Dam, while also ensuring community outcomes are achieved.
In the Opihi Freshwater Management Unit (FMU) an alternative regime is proposed to manage releases of water from the Opuha Dam. Allocation of freshwater has been capped at current rates and partial restrictions are proposed to prevent minimum flows for the river from being breached.
The Temuka FMU is over-allocated and experiences high abstractive pressure. A range of flow and allocation regime is proposed with prohibitions on the transfer of water, increases to minimum flows for the Temuka River and its tributaries, and phasing out of over-allocation through reductions in allocation limits over time (at 3, 5 and 8 year intervals).
The Temuka River is culturally significant to Ngāi Tahu. In recognition of this, an allocation of water (100 litres per second) has been reserved for activities that will enhance mahinga kai outcomes. The allocation would be available from 1 January 2035.
The information below was not released as part of the supporting material when PC7 was notified. At the request of interested parties, this data has been made available during the submission period. The reports which were informed by this data are available under ‘Supporting documents and disciplines’
Water Quality Data for the Opihi and Temuka Catchment
This folder contains the following raw data for the Opihi and Temuka Catchment:
- State of the Environment (SOE) river and lake water quality sampling monitoring from 2017-2019 (XLSX File, 214.83KB)
- SOE Macroinvertebrate data from 2017-2019 (XLSX File, 214.83KB)
- Weekly sampling of bathing sites from 2017-2019 (XLSX File, 214.83KB)
- Temperature data (XLSX File, 214.83KB) and the Terms and Conditions (PDF File, 141.57KB) to be read in conjunction with the datasheet.
Please also note that for sites that are part of NIWA’s national rivers water quality network this must be requested directly from NIWA or from LAWA.
The provisions in Part C of PC7 generally implement the recommendations in the Waimakariri Zone Committee’s ZIPA. Key differences include:
- Some allocation limits proposed in Part C of PC7 are different from those recommended in the ZIPA. The reason for this is that additional technical work was carried out after the ZIPA was finalised in December. This has informed the development of allocation limits.
- A new zone – the ‘Ashley Estuary (Te Aka Aka) and Coastal Protection Zone’ has been introduced and additional restrictions on farming activities and discharges are proposed within this zone. These controls have been included to help with achieving water quality outcomes for the estuary.
Part C of PC7 proposes new nitrogen limits for surface water and groundwater in the Waimakariri sub-region. New rules are proposed to limit the amount of nitrate-nitrogen that enters groundwater. For more information on these proposed rules, see below.
Part C of PC7 includes a framework to manage the diffuse loss of nutrients from farming activities. This is based on the region-wide ‘Red Zone’ framework, but has been modified to ensure outcomes for the Waimakariri sub-region are achieved.
Key differences include a reduction in the area of winter grazing of cattle allowed on a property as a permitted activity, requirements for audited Farm Environment Plans for a larger number of farms, establishment of a Nitrate Priority Area (and Sub-Areas A, B, C, D and E) and a requirement for farms in these areas to reduce nitrogen losses, in stages, and over time.
Lifestyle block owners carrying out farming on small properties (less than 5ha in area) are permitted activities under the proposed framework.
Farms on properties over 5ha may still be permitted, provided they limit the areas used for irrigation and winter grazing of cattle in line with conditions in the proposed rules. Farmers who do not meet these requirements will need to obtain a land use consent, comply with property-based nitrogen limits and implement an audited Farm Environment Plan.
Nitrogen limits only apply to farms which require a land use consent. Farms with a larger area of irrigation or winter grazing than is allowed under the permitted activity rules would need to comply with the ‘Baseline GMP Loss Rate’. The Baseline GMP Loss Rate is a nitrogen limit that reflects activities between 2009 and 2013, but which has been modified to take into account the implementation of Good Management Practice.
Further reductions in nitrogen loss (beyond the Baseline GMP Loss Rate) would be required at 10-year intervals, with the first stage of reduction required to be met by 1 January 2030. The number of stages of reduction required depends on which Nitrate Priority Sub-area the property is located in. The stages of reduction required for each sub-area are:
- Sub-area A – 2 stages
- Sub-area B – 3 stages
- Sub-area C – 4 stages
- Sub-area D – 5 stages
- Sub-area E – 6 stages
The size of the reduction required depends on the type of farming being carried out. Dairy operations are required to reduce nitrogen losses by 15% (at each stage), while all other types of farming are required to reduce by 5% (at each stage).
A staged approach to the reductions takes into account the feasibility of achieving the required reductions and the economic impacts these reductions would have on a farmer.
Detailed modelling indicates that the proposed reductions are sufficient to achieve the nitrogen limits included in the plan change.
Reducing nitrogen losses below the Baseline GMP Loss Rate will be challenging for some landowners. However, economic assessments indicate that these reductions are achievable, and it is anticipated that advances in technology and development of future mitigations will farmers to achieve these reductions.
All farms, including those which have their nitrogen losses managed by an irrigation scheme, would be required to comply with the nutrient management framework in Part C of PC7, including requirements to reduce nitrogen losses in the Nitrate Priority Area.
PC7 proposes water quality limits for drinking water supplies that are consistent with the NZ Drinking Water Standards. In addition, rules in the region-wide section of the LWRP restrict the type of activities that may happen with the protection zone of a Community Drinking Water Supply or a private bore. The nutrient management framework is expected to contribute to reductions in nitrate concentrations in drinking water over time.
New flow and allocation regimes are proposed for a range of surface water bodies in the zone. In general, the revised regimes impose higher minimum flows for surface waterbodies, and as a consequence reliability of supply for water abstractors would probably reduce.
However, Part C of PC7 also sets aside an allocation of water for abstractors that surrender their stream-depleting groundwater or surface water takes in exchange for a deep groundwater take. The availability of this allocation is expected to limit any potential adverse impacts on reliability.
An allocation of water has been reserved from the Ashley River / Rakahuri, Cam River / Ruataniwha and Silverstream rivers in recognition of the cultural significance of these waterbodies. The allocation is available for activities that will enhance mahinga kai outcomes.
Freshwater outcomes proposed for the Waimakariri sub-region are set to maintain current water quality where is good, and improve water quality where it is currently degraded. Improved water quality would mean some rivers in the sub-region would meet national standards for contact recreation, and improvements to habitat would enable further opportunities for customary use and gathering of mahinga kai.
Targeted stream augmentation (TSI) is a system for controlled release of water to improve river and stream flows. Part C of PC7 introduces a regulatory framework that is more enabling than the existing region-wide provisions for TSI.
Augmentation of surface water bodies can provide significant environmental benefits by increasing river flows and reducing concentrations of contaminants.
A key issue with enabling TSI is finding an appropriate source of water to discharge into the subject waterbody, particularly when a number of waterbodies within the Waimakariri sub-region are over-allocated.
Part C of PC7 allows an application for resource consent to be made to take and use water for targeted stream augmentation in over-allocated catchments. In general, the taking of water in an over-allocated catchment would be prohibited, but a pathway has been provided for this particular use in recognition of the overall benefits TSI provides.
The modelling scripts below were not released as part of the supporting material when PC7 was notified. At the request of interested parties, these have been made available during the submission period. The groundwater flow modelling informed technical reports which are available under ‘Supporting documents and disciplines’.
The model was built and run using the FloPy package in Python code. The model files for the groundwater flow model are located in a zip file via the link below. The information also contains a readme file that explains what the files are.
Download the model files
The Ashley Estuary (Te Aka Aka) is a highly sensitive environment. There is high potential for the estuary to become eutrophic, unless additional land use and discharge controls are imposed. Further, significant cultural values are associated with the Ashley Estuary (Te Aka Aka) and Coastal Protection Zone, and additional management responses are necessary to achieve mahinga kai outcomes.
The new rule framework would require farms in the zone larger than 5ha that have winter grazing and/or are irrigated and directly adjoin a surface waterbody to obtain a land use consent to farm. This approach would ensure that the farm is subject to a Farm Environment Plan and regular auditing in order to assess the effectiveness of any measures implemented on farm to reduce contaminant contributions to surface waterbodies.
New policies are also proposed that require discharges of contaminants to surface water to be avoided (where practicable), and where avoidance is not practicable, for the best practicable option to be implemented in order to minimise loss of contaminants.
Map of Coastal Protection Zone
The Ashley Estuary (Te Aka Aka) and Coastal Protection Zone is defined in the LWRP planning maps and shown in the figure below. You can access an electronic version of proposed changes to the Planning Maps here.
It is estimated that the new farming rules proposed by Part C of PC7 would result in an additional 50 land use consents being required (compared with the region-wide rule requirements).
Part C of PC7 extends the region-wide provisions for stock exclusion to include permanently or intermittently flowing springs (waipuna) or open drains and artificial water courses that have surface water in them which discharge into a lake, river or wetland.
Part C of PC7 prohibits access by farmed cattle, deer and pigs into open drains and artificial watercourses (including but not restricted to irrigation canals and water races) within the Ashley-Waimakariri Plains Area. The Area is defined as land that is below 350m above sea level, which is the flatter and more intensively farmed part of the Waimakariri sub-region.
Other sub-region sections of the LWRP (including Selwyn Waihora, Ashburton and South Coastal Canterbury Streams) include similar restrictions to ensure improvements in water quality are achieved.
New policies would direct a review of surface water or stream-depleting groundwater takes that have ‘direct’ or ‘high’ stream depletion effects. Proposed timeframes for reviews are 31 December 2027 (Ashley River /Rakahuri Freshwater Management Unit) and 31 December 2029 (Northern Waimakariri Tributaries Freshwater Management Unit).
Part C of PC7 introduces new requirements for the take and use of surface water and groundwater, including new minimum flows and partial restrictions. However, these minimum flows don’t automatically apply to existing resource consents. New limits introduced by a plan change can only be applied when a resource consent expires, when a new consent is sought, or through a consent review.
Waiting for consents to expire would mean it could take many years before all consents are aligned with new minimum flow requirements. This would slow achievement of ecological benefits and create inequity between abstractors, with some abstractors subject to higher minimum flows before others are.
Common expiry dates ensure all consents in a catchment expire on the same day. This approach enables co-ordinated and integrated planning.
A common expiry date of 2037 is proposed for all resource consents for the use of land / or discharge of nutrients from a farming activity, or the take and use of water. After 2037, consents are proposed to have a 10-year consent duration. These dates align consents with plan review cycles, taking into account realistic timeframes for plans to be made operative following notification.