Under the RMA, there are a number of activities ([1] related to the beds of lakes and rivers, water and discharges) that need to be permitted by a national environmental standard, a rule in a regional plan or a resource consent in order to be undertaken. This means that these activities must have a permitted activity rule or consenting framework available in a regional plan.
This is different to activities on land where if a plan does not mention the activity, it is permitted and there does not need to be a permitted activity rule in a plan.
The land and water plan has many permitted activity rules to ensure low scale, low effects activities do not need to obtain consents.
The Government’s Resource Management (Freshwater and Other Matters) Amendment Bill has proposed changes to Intensive Winter Grazing consent requirements, stock exclusion requirements and the need to consider the Te Mana o te Wai hierarchy of obligations in consent applications. How does this affect the Land and Water Plan and my consent requirements?
Intensive winter grazing and stock exclusion
The Government is proposing to repeal the regulations and conditions for intensive winter grazing from the National Environmental Standards for Freshwater (NES-F) and to repeal the low slope map and associated requirements from the Stock Exclusion Regulations. The Government has signaled that it will be up to regional councils to manage these activities within their region. The Council’s Policy Team is working with Farming Industry bodies to develop rules for these activities in the pLWRP.
For Intensive Winter Grazing in 2024, Council advises the following:
Te Mana o Te wai hierarchy of obligations
The Government’s proposed changes to the National Policy Statement for Freshwater Management (NPS-FM) are to exclude the hierarchy of obligations from resource consenting. Until this Bill becomes law, the Te Mana o Te Wai hierarchy of obligations will continue to be considered in consent applications.
The proposed changes to the NPS-FM do not relate to plan making and the Te Mana o Te wai hierarchy of obligations will continue to be considered in the drafting of the pLWRP.
The rollout of Freshwater Farms Plan in Otago is currently paused. Central Government has indicated that Freshwater Farm Plans will remain but that changes to the system will be made. The details of these changes have not yet been released. Council will adjust to these future changes once they become clear. Council staff will continue to be across changes made by Central Government and will update resources and documents to meet any new or amended legislation, as required.
The use of farm plans as a pathway for a number of farming activities is being considered in the pLWRP. This means that the activities will be able to be managed through the farm plan instead of applying for a consent.
There are no restrictions on when you can apply to replace a consent. If you are applying to replace a consent for substantially the same activity[2], we recommend that you apply at least 6 months before your consent expires. This will allow you to keep operating under your current consent while your application for a replacement consent is being processed by Council. Note: If you do not apply for a replacement consent 6 months before your consent expires there is no guarantee that you can use your current consent once it expires, if a consent decision on your new application has not been made[3].
For example: if your consent expires in April 2025, it is recommended that you have an application lodged and formally accepted by Council by September 2024.
The below are worth considering when deciding whether you lodge a replacement application before or after notification of the pLWRP:
Table 1: Activity status and objective and policy assessment of regional plans at different times in the plan making process
Application lodgement |
Dates |
Activity status of application (i.e. whether it is controlled, restricted discretionary, discretionary or non-complying) |
Objective and policy assessment of Regional Plans |
Application lodged and decided before LWRP notification |
Before end of October 2024 |
Objective and policy assessment of RPW and/or RP:Waste only |
|
Application lodged but not decided before LWRP notification |
Lodged before end of October 2024 and decided after notification date |
Activity status based on RPW and/or RP: Waste rules that applied when the application was lodged |
Objective and policy assessment of RPW and/or RPW: Waste and pLWRP. Weighting to be given to plans based on case law[8] |
Application lodged after LWRP notification and before LWRP is beyond legal challenge/operative |
Lodged after notification date (around end of October 2024) |
Need to consider the RPW and/or RP:Waste and pLWRP rules and the most stringent activity status will apply[9] |
Policy assessment of RPW and/or RPW: Waste and the pLWRP.
Weighting to be given to objectives and policies based on the circumstances and case law[10] |
Application lodged after LWRP is beyond legal challenge/ operative |
Likely to be in 2026/27 |
Only consider the LWRP rules |
Only consider the LWRP objectives and policies. |
We appreciate that it can be confusing identifying what rules apply when. Table 2 below provides advice on what rule would generally apply between the pLWRP being notified and the rules in the pLWRP becoming operative. Questions 7 to 9 below are specific scenarios with further details[11]. For specific advice about your situation please contact consent.enquries@orc.govt.nz.
Table 2: Rules that apply after the pLWRP is notified
Current rule/s for the activity |
Proposed rule/s in the pLWRP |
What needs to be considered between notification of the pLWRP and the rules becoming operative |
Comments |
Permitted |
Permitted |
Both rules including all their conditions need to be complied with |
Check both permitted activity rules. If the new permitted activity rule cannot be met then see the box [Permitted – consent required] below |
Permitted |
Consent required |
If existing use rights apply (see below) the activity only needs to continue meeting the existing permitted activity rules. |
After the new rule is operative there will be 6 months to apply for consent, stop the activity or change the activity to meet the new permitted activity rules. |
Consent required |
Permitted |
Consent will continue to be required |
The permitted activity rules and associated objectives and policies will be considered with weighting when a decision on the application is made |
Consent required |
Consent required |
Consent will continue to be required. The most stringent consent rule will apply. |
Both rules and relevant objectives and policies will be considered with weighting when a decision on the application is made |
You will only need to apply for consents that may be required after the new rules are finalized (operative). From when the rules are finalised, you will have 6 months to either obtain consent, amend your activity to meet the permitted activity standards, or cease the activity.
The RMA provide for activities to continue to operate under existing use rights while the new land and water plan is being considered. These existing use rights apply when:
It is likely that the land and water plan will not be operative until 2026 or beyond. To support you in applying for consent, when it is time to do so, Council will prepare application forms, guidance materials and hold workshops.
Table 2 provide a checklist for to determine if you have existing use rights.
Table 2: Checklist for existing use rights
Is the activity lawfully established |
|
Has the activity been occurring since notification of the land and water plan with no breaks longer than 6 months |
|
Is the activity the same as before notification of the land and water plan |
|
Is the activity currently permitted or no consent is required |
|
Is consent required under the land and water plan |
|
Note: If you seek to start a new activity that was not existing before the pLWRP was notified then you will need to consider the rules in the pLWRP for that activity. If consent is required, you will need to apply and obtain this before commencing the activity.
E.g. If you have an existing feedlot and can meet Table 2 you will have existing use rights but if you decide to construct a feedlot and this is not in use before the pLWRP is notified you will need to obtain consent if you cannot meet the permitted activity rules in the pLWRP.
The Council will provide direction and advice on consenting requirements for specific activities once the pLWRP is notified.
Refer to the checklist above. This approach applies to all permitted activities that would become consented under the land and water plan.
If your current take was lawfully established, water is continued to be taken (with no breaks longer than 6 months) and there is no change to the maximum rates and volumes of water taken and what the water is used for, then you can continue to operate under the permitted activity rule in the Regional Plan: Water until the land and water plan is operative.
Once the pLWRP is operative, you must apply for a consent within 6 months, amend your activity to meet the permitted activity rule or cease the activity. If you lodge a consent application, you can then continue to operate under the permitted activity rule in the Regional Plan: Water until your consent application is granted.
If you can currently undertake activities using the permitted activity rules of the RPW or RP:Waste and if the pLWRP also makes your activity permitted, once the land and water plan is notified you will need to consider both plans’ permitted activity rules. You will need to make sure you are meeting all parts/conditions of each permitted activity rule in order for the activity to be permitted.
If you cannot meet the new permitted activity rule in the land and water plan, you will need to apply for a consent within 6 months of the rule becoming operative (see 7 and 8 above) or change the way you undertake your activity to meet the permitted activity conditions.
You need to consider both the current and proposed permitted activity rules and meet both to be permitted until the new permitted activity rule is finalised.
If the activity you are undertaking has permitted activity criteria under the notified plan and you can’t meet one or some of those criteria, you can apply for resource consent to do the activity. The timing of when you need consent depends on the rule.
When new rules are notified and are going through the submissions and hearing process, existing activities can carry on as they were. Six months after any new rules become operative (which means after any appeals are settled and could be as far away as 2026), existing activities need to:
The exception to this is activities that already have a resource consent, such as a water take – those can continue until the existing consent expires or is reviewed.
For more information, please see:
Practice Note: Consenting under Proposed and Operative Plans
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
We are actively looking at the most efficient way to manage effects on the environment, and Freshwater Farm Plans might be one of those opportunities we can leverage. Given lots of people will need them, we are keen to hear your feedback on what we could include as part of a Farm Plan.
Freshwater Farm Plans are very useful to improve environmental performance, particularly in tailoring actions to individual farms so that ‘good management practices’ are adopted. However, the science investigations have shown that in some areas of the region, ‘good management practices’ will not address declining water quality trends or result in the more substantial water quality improvements required.
At this stage, it seems unlikely that Freshwater Farm Plans can achieve that on their own.
In those situations, resource consents will likely be needed, alongside Freshwater Farm Plans, to push for more significant reduction in contaminant losses. However, it is still important that we get feedback on the types of activities you think could be managed through Freshwater Farm Plans, noting this may not be able to apply everywhere and for everything.
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
There are a wide range of setback requirements in the draft plan. The setbacks vary, depending on the kind of activity, the level of risk, and the level of environmental improvement required. In general, they ensure that activities or structures that pose a risk to water quality (such as discharges of effluent to land, cultivation, or wastewater treatment plants) do not take place or are not established in a location that is too close to waterbodies.
For farming activities, one of the biggest sources of contaminants is overland flow of water into waterbodies, when that water contains, or has the opportunity to pick up sediment, dung and other contaminants. A setback (preferably vegetated), usually varying in width depending on the slope, is one way to filter out these contaminants. Some higher-risk activities, such as intensive winter grazing and sacrifice paddocks, have large areas of exposed soil in winter, and are a high risk of sediment and dung getting into waterbodies, unless there is some separation.
Typical setbacks for farming activities are:
For forestry planting, the setbacks are intended to provide for some protection of water quality at all stages of the forestry process, acknowledging that if trees are setback from waterbodies, related activities, such as harvesting are less likely to occur close to waterbodies. The setbacks will also protect waterbodies from some of the effects of standing trees, such as shading. Within the setback, riparian planting will be able to occur. At this stage the setbacks are 20m for forestry on slopes less than 10 degrees and 50m for above 10 degrees.
We are looking at ways that the setbacks can be refined, while still providing the environmental improvements required and are keen for your feedback on this. For example, this may come with greater emphasis on critical source areas for farming activities, or slash and sediment management for forestry.
The way the rules have been designed mean that if you can't or don't want to meet the setbacks, you can apply for consent to undertake your activity closer than the setbacks state. The consent would put mitigations in place to ensure the risk was adequately managed. We are also looking into whether a Freshwater Farm Plan can be used as an alternative to some of these setback requirements – your feedback on the ways this could work is sought.
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
Sacrifice paddock is defined in the National Environmental Standards for Freshwater (NES): as an area on which —
(a) cattle are repeatedly, but temporarily, contained (typically during extended periods of wet weather); and
(b) the resulting damage caused to the soil by pugging is so severe as to require resowing with pasture species
The rule has been included because it is an activity that is highlighted in the NES, and in the Environment Court considering Southland’s plan.
Sacrifice paddocks are used to reduce soil damage on large areas of the farm and minimise other risks to the environment and animal welfare. The use of sacrifice paddocks is infrequent and for short periods of time (i.e. as a planned back-up option for bad weather or other circumstances).
Risks associated with sacrifice paddocks are similar to those of intensive winter grazing and pasture-based wintering – pugging, run-off into waterways, devegetation, loss of soil armouring and delays to pasture regrowth.
The time limit (the use of a sacrifice paddock should not exceed a total of more than 60 days in any 12month period) is based on the fifth interim decision of the Environment Court (23 December 2022) on the proposed Southland Water and Land Plan. It is understood that sacrifice paddocks are not used consistently over long periods of time (then it would become pasture-based wintering). Similarly, the size limit (5 ha for landholdings less than 500ha, or 1% or up to 30ha for landholdings greater than 500ha, whichever is lesser) is based on the Southland Environment Court Decision.
We are keen to understand if sacrifice paddocks are always part of an intensive winter grazing operation and can be managed as part of that existing consenting process, or if there is a better way of managing the activity.
We are also keen to hear if the time limits and/or size restrictions are workable for Otago.
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
The current permitted volume (20 m³/month, 240 m³/year) results in large quantities of gravel extraction, with no oversight by council because consent is not required. While gravel extraction can be useful in managing a river’s flood carrying capacity, it can negatively impact the river’s health when not managed well. We think the current volume is too high to be sure it’s not impacting the health of the river.
The smaller volume (5 m³ in any 12 consecutive months) will retain some ability to extract gravel at a level that should not impact river health. A consent will be required for larger extractions, to enable the inclusion of site-specific good practice type conditions and ensure that the health of the river can be maintained.
This conservative approach is an interim step, while additional work is undertaken to improve our knowledge of gravel across Otago. In the longer term, it is intended that there will be greater guidance for gravel extractions, which may support larger permitted volumes in some waterbodies.
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
Typically, reductions in water allocation to ensure that the total consented allocation in a catchment is, overtime, brought in line with the relevant take limits in the LWRP will be done through the consent replacement process. (The RMA specifies that a consent authority may review the conditions of consent to align the levels, flows, rates or standards set by a regional rule with consent conditions. However, the RMA does not give the Council the power to cancel a consent upon review, and only allows Council to reduce the amount taken by a certain extent.)
The first step in reducing water allocation to ensure that the consented allocation in a catchment is brought in line with the relevant take limit is by removing “paper” allocation. This means that when a consent holder applies for a new resource consent to replace an existing one, ORC will only allocate a quantity of water that does not exceed the historic actual use of water under the previous consent and that reflects reasonable and efficient use of that water.
Where removing “paper” allocation will not be sufficient to achieve the take limit, reductions in water allocation will need to occur in stages. During the first stage (i.e. first consent replacement process) “paper” allocation will be removed. During the second stage further reductions will need to be achieved through either the implementation of a community-led proposal for achieving the take limit (for example through water sharing) or, alternatively, through pro rata claw backs across the different users.
ORC seeks to improve the accuracy of future technical work that informs the development of regulatory and non-regulatory approaches for managing nutrients and other contaminants in the region. The information provided in Freshwater Farm Plans can help ORC developing a better understanding of how farming contributes to overall loadings and make sure that these management approaches are effective.
ORC will make sure that any such information provided through the Freshwater Farm Plans will be treated confidentially and will not be made available to the public (unless it is aggregated and or shared in a manner that does not allow for the source of this information (i.e. the individual farm) to be identified.
Dairy support is one of the more intense activities that can occur on a farm and often has a higher risk of contaminant losses to the environment. If water quality is to be maintained where it is good, and improved where it is poor, a first step needs to be keeping a close watch on activities that might result in an increase of losses – hence the need for a resource consent for any new or increased area of dairy support.
There is a region-wide rule that requires resource consent for new or increased areas of dairy support. The application would need to show how losses of contaminants from the farming operation will be reduced.
Existing dairy support can continue under a Freshwater Farm Plan, unless it is in an area that requires consent for dairy or dairy support (currently proposed to be Taiari/Taieri, North Otago, Dunedin and Coast FMUs, and Manuherekia and Lower Clutha rohe). These areas have been identified because they have more water quality challenges that need to be addressed.
The definition of pasture-based wintering means break feeding cattle, other than lactating dairy cows, on pasture between 1 May and 30 September inclusive where supplementary feed offered is more than 10,000 kgDM/ha.
This is based on the fifth interim decision of the Environment Court (23 December 2022) from the proposed Southland Water and Land Plan.
Pasture-based wintering is the supplementary feeding of cattle that are grazing on pasture over winter. It is distinguished from intensive winter grazing where stock graze on fodder crops as well as supplementary feed. Sheep are excluded from this definition – we are interested in your views on that.
Grazing cattle on pasture over winter has the potential to generate adverse environmental effects, including sediment run-off into waterways, devegetation, loss of soil armouring and delays to pasture regrowth. The risk arising from such grazing on pasture is generally related to how intensively the pasture is grazed, hence the threshold on how much introduced feed there is. At high levels of introduced feed, the risk can become similar to the risks from intensive winter grazing on forage crops (where grazing leaves little or no residual cover).
Based on the Environment Court’s direction for Southland, we think we should be managing this activity and are keen to understand the implications of the rule for Otago.
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
The intention of this threshold was to be able to look more closely at those farms that were applying comparatively high levels of synthetic nitrogen fertiliser. We understand that very few Otago farms breach the 190kg/ha/yr NES cap of synthetic nitrogen fertiliser. In some areas of Otago (some specific FMUs or parts of FMUs), there is a need to reduce the amount of nitrogen entering waterbodies, and in some other areas the trend for nitrogen in waterbodies is getting worse. A 190kg/ha/yr threshold for synthetic nitrogen fertiliser is unlikely to help address this problem, as it doesn’t affect many farms.
The 190kg/ha/yr cap in the NES is a firm ‘cap’. In the draft Plan, a lower threshold is suggested, but it is not a ‘cap’: it will trigger a resource consent, which will allow a more focussed look at how contaminant losses can be reduced. This will likely require implementation through specific provisions in a Freshwater Farm Plan.
We are still looking at whether 100kg/ha/yr N is the right threshold, and we welcome your feedback. By way of context, for the case study dairy farms in the economic profile work, the average nitrogen fertiliser use was 142kg/ha/yr and the median was of 124kg/ha/yr. For sheep and beef farms, most used less than 30kg/ha/yr of nitrogen fertiliser on pastures.
The stocking rate was included as a proxy for intensity. The stocking rate of 2.5 cows per hectare is based on what the maximum stocking rate might be for a farm to be self-sufficient in terms of feed (e.g. if it was a finishing sheep and beef farm). It is intended to be a generous interpretation of the basic level needed for efficient pasture management (2.5 cows is roughly equal to 20+ livestock units – a ewe with a lamb at foot). It is not intended to be representative of current stocking rates, which vary across the region. At or below this level, a controlled activity resource consent will be required (likely to be those farms where less than 20% of feed is imported i.e. system 1 to system 3 dairy farms). A controlled activity means consent must be granted, and we can impose conditions on the matters identified as being controlled.
It is worth keeping in mind that this stocking rate is for a farm’s total area, not effective area. We agree that it may not be best to use a single threshold across all areas of Otago, and welcome suggestions of alternatives.
More stringent requirements are needed for more intense land uses (likely to be those where 20% or more of feed is imported i.e. some system 3, system 4 and system 5 dairy farms). More focussed reduction of losses is likely to be required from farming that has higher risk or losses.
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
In general, if both activities were occurring on the same property, that could be covered by a single consent, along with any other activity that required consent. In fact, it would be ORC’s preference to bundle all your activities together and get one application that covered everything.
For dairy farming and dairy support, there are region-wide rules that require resource consent for any new or increased area, much like the current National Environmental Standard for Freshwater.
In some areas, where water quality pressures are lower, existing dairy farming and dairy support can continue under a Freshwater Farm Plan. In other areas, where more significant water quality improvements are required, or there are declining trends in water quality, existing dairy farming and dairy support will require a resource consent, and more focussed reduction of losses is likely to be required.
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
Sacrifice paddock is defined in the National Environmental Standards for Freshwater (NES): as an area on which —
(a) cattle are repeatedly, but temporarily, contained (typically during extended periods of wet weather); and
(b) the resulting damage caused to the soil by pugging is so severe as to require resowing with pasture species
The rule has been included because it is an activity that is highlighted in the NES, and in the Environment Court considering Southland’s plan.
Sacrifice paddocks are used to reduce soil damage on large areas of the farm and minimise other risks to the environment and animal welfare. The use of sacrifice paddocks is infrequent and for short periods of time (i.e. as a planned back-up option for bad weather or other circumstances).
Risks associated with sacrifice paddocks are similar to those of intensive winter grazing and pasture-based wintering – pugging, run-off into waterways, devegetation, loss of soil armouring and delays to pasture regrowth.
The time limit (the use of a sacrifice paddock should not exceed a total of more than 60 days in any 12month period) is based on the fifth interim decision of the Environment Court (23 December 2022) on the proposed Southland Water and Land Plan. It is understood that sacrifice paddocks are not used consistently over long periods of time (then it would become pasture-based wintering). Similarly, the size limit (5 ha for landholdings less than 500ha, or 1% or up to 30ha for landholdings greater than 500ha, whichever is lesser) is based on the Southland Environment Court Decision.
We are keen to understand if sacrifice paddocks are always part of an intensive winter grazing operation and can be managed as part of that existing consenting process, or if there is a better way of managing the activity.
We are also keen to hear if the time limits and/or size restrictions are workable for Otago.
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
Leachate from silage storage is full of nutrients, especially nitrogen. It is highly concentrated and extremely damaging to waterways and can contaminate groundwater. To manage this risk, two options for a volume threshold are included, which will require larger storage facilities to obtain resource consent.
The initial figure corresponded with the volume for storing other organic waste. Feedback (from Council) indicated that this was too small, and we have offered two options: 250m³ and 500m³. The intention is that smaller to medium pits/stacks would be permitted while larger pits/stacks (which generally indicate a larger operation or more intense land use) would require consent.
We are actively considering both whether there should be a threshold, and if so, what it should be, so welcome feedback on this.
A third option may be permitting any size silage storage where there is an impervious base and the leachate is captured and goes into a farm effluent system or is captured and spread via effluent spreaders or slurry tanker. This could better manage low-risk silage storage.
If you have questions that couldn’t be answered today or you want to get in contact with Otago Regional Council, please feel free to call us on 0800 474 082 and ask for the Land and Water Policy team, or email policy@orc.govt.nz.
In 2019, the Minister for the Environment told Otago Regional Council we could do better to manage Otago's lakes, rivers and streams and directed us to prepare a new regional policy statement and land and water plan by the end of 2023.
We are now developing a plan to set new rules and regulations on how we as a community do this. Mana whenua, the kaitiaki of our land, has joined us in this journey.
This new plan will align with the Government goal to improve water quality within one generation.
The new plan will become a powerful planning tool to manage land and waterways in the region. It will bring change in the status quo, and this will affect people. When the impacts of the new plan start to be felt in the years ahead, you’ll want to understand it and feel you have contributed to it.
Te Mana o te Wai - vital importance and health of our water - is part of Otago’s collective well-being and future sustainability. The health of some our waterways is excellent, but others need improving. This is important because Otago’s waterways support all life from threatened native fish, the mahika kai we collect and the swimming holes we love, to how we earn our living and enjoy clean groundwater.
Te Mana o te Wai is respecting and looking after the water, so the water can look after you. It also recognises that mana whenua, councils, water users and the wider community all have a role in managing freshwater.
The new Land and Water Plan will be based on a whole-of-catchment approach - ki uta ki tai (from the mountains to the sea) - that is consistent with Te Mana o te Wai and prioritises the health and well-being of water bodies.
ORC and rūnaka have worked in partnership on developing the Land and Water Regional Plan, at governance and working levels, so that content represents the aspirations of Māori/iwi.
To reflect Otago’s environment, we divided the region into five Freshwater Management Units (FMU). The Clutha Mata-Au FMU, being quite large, is further divided into five rohe, which means "area" in te reo.
An FMU is a water body or water bodies of a manageable size for setting freshwater objectives and limits. This can be a river, a part of, or a group of catchments. All regional councils are required to set FMU.
You can find your FMU/rohe here.
We will keep all information up to date on our website.
While the LWRP is still a draft plan, it was important that we engage with Otago communities to get their feedback before we finalised the plan. Key information contained in the plan, including proposed impacts was available on our website for this.
In November 2021 and March 2022, we wanted to find out which waterbodies (lakes, rivers, streams, wetlands) are most important to you, what you value most about them and what characteristics are key and received feedback from more than 560 people.
Of your feedback, these values were strongest:
Other values included:
Thank you to everyone who provided feedback or came along to one of the community meetings in our first two rounds of engagement to tell us what you want for land and water resources in our region.
More information on the feedback from rounds one and two can be found here.
Once the feedback has been collated, ORC will review and reflect on all materials and these will be used to inform development of the final LWRP. This draft Plan is shared with ORC councillors in December 2023.
Drop-in sessions, online discussions and an online feedback form were offered to give anyone the chance to share their feedback. This closed 6 November 2023.
The Council realises that improving freshwater outcomes will mean change, and that can have impacts for the economy. That is why it was important to do our homework ahead of time.
The Council worked together with industry groups on the economics and made sure we used real farms and growing operations from across Otago to understand the importance of fresh water.
This included giving people from across Otago a voice in how the impacts of different policy options is understood - this was done through the creation of Catchment Stories.
incorporate these into the paragraphs rather than external reference.
[1] related to the beds of lakes and rivers, water and discharges
[2] For further information on this refer to: Exercising your consent after it expires - Practice note
[3] For further information on this refer to: Exercising your consent after it expires - Practice note
[4] Copies of the oRPS and pRPS can be found here: Otago Regional Policy Statements (orc.govt.nz)
[5] For further information on this refer to: Consenting under proposed and operative plans
[6] RPW is Regional Plan: Water for Otago: Regional plan - Water (orc.govt.nz)
[7] RP:Waste is Regional Plan: Waste for Otago: Regional plan - Waste (orc.govt.nz)
[8] Key elements from case law: (1) the extent to which the proposed measure has been exposed to independent decision making (2) possible injustice to the applicant (3) the extent to which a new measure may represent a significant policy shift when compared to the provisions of the operative plan, or implement a coherent pattern of objectives and policies in a plan (4) Where there has been a significant shift in Council policy, and any new provisions accord with Part II of the RMA or the requirements of a national policy statement – then the objectives and policies in the proposed plan change may potentially be given more weight
[9] E.g. if in the RPW the activity is restricted discretionary activity but in the pLWRP the activity is discretionary, the activity will be processed as a discretionary activity.
[11] For further information on this refer to: Consenting under proposed and operative plans
[12] Lawfully established means that when the activity commenced it was compliant with all the relevant planning rules and regulations at that point in time e.g. it met any permitted activity rules that applied.
[13] The nature of the activity and when it is typically undertaken will be taken into consideration for this requirement. For a seasonal activity (e.g. Intensive Winter Grazing), the normal year round operation will be the basis for whether the activity has stopped or not.
[14] More information on when the RPW applies can be found here: National Environmental Standards for Plantation Forestry (NES-PF) (orc.govt.nz)
Term |
Definition |
7-day mean annual low flow (MALF)
|
The average, for a number of years, of the lowest average flow over seven consecutive days in each year. The lowest average flow over seven consecutive days in each year is determined by calculating the average flow over seven consecutive days for every seven consecutive day period in the year and choosing the lowest. |
Agrichemical |
Any substance whether inorganic or organic, man-made or naturally occurring, modified or in its original state, that is used to eradicate, modify, or control flora and fauna. For the purpose of this Plan, it includes agricultural compounds, but excludes oral nutrition compounds, vertebrate toxic agents, and fertilisers. |
Agricultural solid waste |
Agricultural waste that exhibits the properties of a solid, e.g., it can be stacked and hold a definite angle of repose. For the purposes of the Plan, if any waste does not meet the definition of agricultural solid waste it is treated as agricultural liquid waste. |
Agricultural waste |
The waste from the customary and generally accepted activities, practices, and procedures that farmers and producers adopt, use, or engage in during the production and preparation for market of poultry, livestock, and associated farm products; and in the production and harvesting of agricultural crops that include agronomic, horticultural, silvicultural, viticultural and aquaculture activities. In addition, winery wastewater and grape marc constitutes agricultural waste. |
Animal effluent storage facility |
A pond, tank, or structure primarily used for the containment or storage of animal effluent, but excludes any ancillary structures for the collection, conveyance, or treatment of liquid or solid animal effluent, such as sumps, stone traps and weeping walls. |
Animal effluent system |
The collection, storage, or treatment, of liquid or solid animal effluent. |
Aquifer pump testing |
A test made by pumping a well for a period of time and observing the change in water level or pressure in the aquifer. A pumping test may be used to determine the capacity of the well, the hydraulic characteristic of the aquifer or any interference effects. |
Artificial water course |
A watercourse that is deliberately created by human action (including an irrigation canal, water supply race, canal for the supply of water for electricity power generation, farm drainage canal, drain, or duck pond) provided that it is not part of a water body or a modified watercourse. |
Available reticulated wastewater system |
A community or municipal reticulated wastewater system which: (1) passes within 30 metres of the property boundary: or, (2) passes 60 metres of the closest building on a property; and (3) the system has existed in that location for more than 12 months. |
Biosolids |
Sludge derived from a wastewater treatment plant that has been treated and/or stabilised to the extent that it is able to be safely and beneficially applied to land. |
Cascading hazards |
Where the occurrence of one natural hazard is likely to trigger another natural hazard event e.g., an earthquake triggering a landslide which dams a river causing flooding. |
Classifiable dam |
A dam that: (a) has a height of 4 or more metres and stores 20,000 or more cubic metres volume of water or other fluid; or (b) has a height of 1 or more metres and stores 40,000 or more cubic metres volume of water or other fluid. For the purpose of this definition: (a) the height of the dam is the vertical distance from the crest of the dam and must be measured: (i) in the case of a dam across a water body, from the natural bed of the water body at the lowest downstream outside limit of the dam; and (ii) in the case of a dam not across a water body, from the lowest elevation at the outside limit of the dam; and (iii) in the case of a canal, from the invert of the canal; and (b) in measuring a dam’s stored volume, the stored volume of water or other fluid does not include: (i) in the case of a dam across a water body, water or fluid that is lower than the natural ground level at the lowest downstream outside limit of the dam; and (ii) in the case of a dam not across a water body, water or fluid that is lower than the natural ground level at the lowest elevation at the outside limit of the dam; and (iii) in the case of a canal where the canal invert (the lowest point of the inside of the canal structure that stores water or fluid) is below the natural ground level, water or fluid that is lower than the natural ground level at the lowest elevation at the outside limit of the canal structure. |
Climate change adaptation |
The process of adjustment to actual or expected climate and its effects. |
Climate change mitigation |
A human intervention to reduce the sources of, or enhance the sinks of, greenhouse gases. |
Closed landfill |
Any landfill that no longer accepts solid waste for disposal. |
Community water supply |
Water taken and used primarily to supply drinking water to users via a reticulated system, with water also supplied for other purposes including institutional, industrial, and commercial processing, cultivation, and production of food and beverages and fibre, animal drinking water purposes, amenity irrigation use and fire-fighting activities. The supply of domestic water must constitute at least 50% of the water supplied. |
Composting toilet |
A toilet system that uses a predominantly aerobic processing system that treats human excreta, typically with no water, via composting or managed aerobic decomposition. |
Construction phase stormwater |
Water, sediment, and entrained contaminants resulting from precipitation on exposed or unstabilised land and which arises from construction or demolition activities, or the development of land. |
Controlled lake |
A lake that is located within the bed of a river where the outflow of the lake is controlled by artificial means. |
Cross-mixing |
The introduction of water from one water body into another water body, where there is no natural connection between those water bodies. |
Cultivation |
Preparing land for growing pasture or a crop by mechanical tillage, direct drilling, herbicide spraying, or herbicide spraying followed by over-sowing for pasture or forage crops (colloquially referred to as ‘spray and pray’), but excludes: (a) herbicide spraying undertaken solely for the control of pest plant species. |
Dairy Effluent Storage Calculator |
The Dairy Effluent Storage Calculator available from http://www.dairynzdesc.co.nz |
Dam |
A structure used or to be used for the purpose of impounding water (and any substances dissolved in, suspended, or otherwise combined with the water) or water body. |
Damming |
The activity of impounding water (and any substances dissolved in, suspended in or otherwise combined with the water). |
Dewatering |
The abstraction of groundwater so as to lower the water table: (a) for the period of time required to enable excavation, construction, maintenance, or geotechnical work to proceed in the dewatered area; or (b) to sustain a lower localised water table. |
Diversion |
The purposeful redirecting of water flow from its natural or existing direction of flow. For the purposes of this Plan, taking water from the bed of any water body, even if only for a short distance before it is returned, is considered a take and discharge. |
Drilling |
A method of boring a hole into the ground predominantly by rotating, percussive or washing action. Excludes excavation of pits by digging, blasting or other forms of excavation, driven posts or driven solid pile. |
Effects management hierarchy (in relation to indigenous biodiversity) |
The effects management hierarchy set out in ECO-P6 of the ORPS. |
Effects management hierarchy (in relation to natural inland wetlands and rivers) |
The effects management hierarchy set out in LF-FW-P13A of the ORPS. |
Environmental flows and levels |
Any minimum flows, management flows, environmental levels and minimum levels identified in this Plan that apply to a waterbody. |
Environmental level |
The water levels, when measured at the relevant water level monitoring site, within which a lake must be maintained, and may include minimum levels and maximum operating levels. |
Existing resource consent |
1. resource consent which has been given effect to 2. resource consent which has not been given effect to and has not lapsed; and 3. an expired resource consent continuing to be exercised under s124 of the RMA. |
Feedlot |
This has the same meaning as in the National Environmental Standards for Freshwater 2020: A stockholding area where cattle — (a) are kept for at least 80 days in any 6-month period; and (b) are fed exclusively by hand or machine. |
Flood protection and drainage infrastructure |
Any infrastructure owned or managed by ORC exercising its powers, functions and duties under the Soil Conservation and Rivers Control Act 1941, the Land Drainage Act 1908, or the Local Government Act 1974, in relation to flood control and drainage. |
Flood protection and drainage infrastructure works |
Any works undertaken by or on behalf of ORC for the purpose of establishing, maintaining, altering, or removing any flood protection and drainage infrastructure. |
Fractured rock aquifers |
An aquifer which stores and transmits water through crevices, joints and fractures in an otherwise impervious rock mass, as shown in [a map to come]. |
Freshwater Management Units (FMUs) and rohe |
Otago is divided into five Freshwater Management Units (FMUs). An FMU is a water body or multiple water bodies of a manageable size where freshwater objectives and limits will be set. Rohe means ‘area’ in te reo, and is used to define distinct areas within larger FMUs. |
Hāpua (lagoon) |
A pool of water, lagoon, pond. |
Hard protection structure |
Within the coastal environment, this has the same meaning as in the Glossary of the New Zealand Coastal Policy Statement 2010 as set out below: Includes a seawall, rock revetment, groyne, breakwater, stop bank, retaining wall or comparable structure or modification to the seabed, foreshore or coastal land that has the primary purpose or effect of protecting an activity from a coastal hazard, including erosion. Outside the coastal environment, this means any structure that has the primary purpose of natural hazard risk mitigation, including: dams, weirs, riprap, stop banks, carriageways, groynes, or reservoirs. |
Hazardous Substances and New Organisms (HSNO) Act |
The Hazardous Substances and New Organisms (HSNO) Act is a law that manages the risks that hazardous substances and new organisms pose to the health and safety of people and communities and the New Zealand environment. |
In-stream dam
|
Any dam which is located in part or in whole in, on, under or over the bed of a lake or river, or within a natural inland wetland. |
Indigenous vegetation |
Vascular and non-vascular plants that, in relation to a particular area, are native to the ecological district1 or freshwater or marine bioregion in which that area is located. |
Kaitiakitaka |
Māori Environmental Management. |
Ki uta ki tai |
The Land and Water Regional Plan will be based on a whole-of-catchment approach - ki uta ki tai - from the mountains to the sea. |
Lawfully established |
Established in accordance with and compliant with the Resource Management Act 1991 or any former legislation at the time of establishment. |
Line |
A wire or conductor (including a fibre optic cable) used or intended to be used for telecommunications or the transmission of electricity. |
Liquid animal effluent |
Faeces and urine from land-based animals, including associated process water, wash-down water, contaminants and sludge but excluding solid animal effluent. For the purposes of this definition, it does not include incidental animal effluent present in livestock processing waste streams. |
Mahika kai |
Gathering of food and natural materials by Kāi Tahu whānui in accordance with tikaka, the places where those resources are gathered, and the work, methods and cultural activities involved in obtaining them. |
Main stem |
In relation to rivers, the rivers identified in [a schedule to come] of this Plan and applies from the source of that course to the sea or confluence with another main stem but excludes any tributary. |
Management flow |
The flow, when measured at the relevant flow monitoring site, at which the taking of water from a water body is subject to reductions. |
Mātaitai reserve |
Mātaitai reserves are identified traditional fishing grounds tangata whenua have a special relationship with. |
Minimum flow |
The flow, when measured at the relevant water flow monitoring site, at which the taking of water from a water body must cease. |
Minimum level |
The water level, when measured at the relevant water level monitoring site, at which the taking of water from a water body must cease. |
Modified watercourse |
A water body that has been modified, channelled, or straightened for land drainage or other purposes. |
National Environmental Standards for Freshwater (NES-F) |
National Environmental Standards for Freshwater (NES-F). The standards regulate activities that pose risks to the health of freshwater and freshwater ecosystems. |
National Objectives Framework (NOF) |
The National Objectives Framework (NOF) sets the necessary values, outcomes and specific attributes required to meet the hierarchy of obligations and local definitions of Te Mana o Te Wai, and enable long-term visions to be realised. |
National Policy Statement on Freshwater Management (NPS-FM) |
The Government’s National Policy Statement on Freshwater Management (NPS-FM) 2020 gives effect to new protection we must give to our waterways. |
Natural lake |
A lake that is not a controlled lake or an off-stream artificial lake. |
Non-consumptive take
|
A take of water from a water body where the same volume of water is returned: (a) to the same water body; and (b) at the same time or within a timeframe as near as practicable to when the take is operating. |
Off-stream artificial lake |
A lake that is located outside of the bed of a river and that is not part of a water body. |
Off-stream dam |
Any dam of which no part is located in, on, under or over the bed of a lake or river, or within a natural inland wetland. |
On-site wastewater treatment system |
A system that receives wastewater or sewage from a single landholding and treats and applies the wastewater or sewage to a land application system on the same property. |
Organic waste |
Biodegradable vegetative material which includes compost and green waste and does not include any sewage, greywater, industrial or trade waste or agricultural waste. |
Paper Allocation/Paper Water |
Paper allocation is any quantity of water that is allocated under a resource consent but that exceeds the actual (recorded) rate of take or volume of water taken by the consent. |
Pasture-based wintering |
Break feeding cattle, other than lactating dairy cows, on pasture between 1 May and 30 September inclusive where supplementary feed offered is more than 10,000 kgDM/ha (fresh weight (grams) x dry matter percentage (as a decimal) x hectares). |
Permanent forest or permanent forestry |
A forest deliberately established (including through planting or facilitated regeneration) without any intention to harvest, including for the purpose of creating a biological carbon sink, that: (a) comprises an area of at least 1 hectare of continuous forest cover, but (b) does not include: (i) plantation forestry; (ii) forest species in urban areas; or (iii) nurseries and seed orchards; or (iv) trees grown for fruit or nuts; or (v) willows and poplars space planted for soil conservation purposes. |
Pit toilet |
A hole in the ground used for the disposal of sewage, also referred to as a long drop or pit latrine. |
Plan Change 1 (PC1) |
Plan Change 1 amended the Regional Plan: Waste for Otago by:
|
Plan Change 8 (PC8) |
Plan Change 8 made a range of amendments to the current water and waste plan provisions to better manage specific urban and rural activities, known to be contributing to water quality issues in parts of Otago. The rural discharge provisions made operative are set out in the following parts of Plan Change 8:
|
Potentially contaminated |
Part of a site where an activity or industry described in the Ministry for the Environment’s Hazardous Activities and Industries List (October 2011) has been or is being undertaken on it or where it is more likely than not that such an activity or industry is being or has been undertaken on it, but excludes any site where a detailed site investigation has been completed and reported and which demonstrates that any contaminants in or on the site are at, or below, background concentrations. |
Proposed Otago Regional Policy Statement 2021 (pORPS) |
The Proposed Otago Regional Policy Statement 2021 (pORPS) sets the direction for future management of Otago's natural and physical resources. |
Rakatirataka |
Leadership, authority, and decision-making powers. |
Reasonable mixing |
The mixing that occurs in a mixing zone as defined in APP[RWS] of this Plan. |
Regionally significant infrastructure |
(1) roads classified as being of regional importance in accordance with the One Network Framework, (2) electricity sub-transmission infrastructure, (3) renewable electricity generation facilities that connect with the local distribution network but not including renewable electricity generation facilities designed and operated principally for supplying a single premise or facility, (4) telecommunication and radiocommunication facilities as respectively defined in section 5 of the Telecommunications Act 2001 and in section 2 of the Radiocommunications Act 1989, (5) facilities for public transport, including terminals and stations, (6) the following airports: Dunedin, Queenstown, Wānaka, Alexandra, Balclutha, Cromwell, Ōamaru, Taiari. (7) navigation infrastructure associated with airports and commercial ports which are nationally or regionally significant, (8) defence facilities for defence purposes in accordance with the Defence Act 1990, (9) community drinking water abstraction, supply treatment and distribution infrastructure that provides no fewer than 25 households with drinking water for not less than 90 days each calendar year, and community water supply abstraction, treatment and distribution infrastructure (excluding delivery systems or infrastructure primarily deployed for the delivery of water for irrigation of land or rural agricultural drinking-water supplies) (10) community stormwater infrastructure, (11) wastewater and sewage collection, treatment and disposal infrastructure serving no fewer than 25 households, (11A) oil terminals, bulk fuel storage and supply infrastructure, and ancillary pipelines at Port Chalmers and Dunedin, and (12) Otago Regional Council’s hazard mitigation works including flood protection infrastructure and drainage schemes.
For the avoidance of doubt, any infrastructure identified as nationally significant infrastructure is also regionally significant infrastructure. |
Regionally Significant Wetland |
A Regionally Significant Wetland is any wetland that has one or more of the following values:
|
Reticulated wastewater system |
A wastewater treatment plant and the attached network of structures including pipes and pump stations owned and operated by a group, institution, territorial authority or company that primarily treats wastewater from more than one site. |
Riparian margin |
The land within 10 metres of the bed of a lake or continually flowing river (measured horizontally). |
Sacrifice Paddock |
This as the same meaning as in the National Environmental Standards for Freshwater 2020: An area on which — (a) cattle are repeatedly, but temporarily, contained (typically during extended periods of wet weather); and (b) the resulting damage caused to the soil by pugging is so severe as to require resowing with pasture species. |
Secondary take |
The taking of water that has previously been taken from one water body and discharged to another, for the purpose of supplying the secondary take. |
Sediment trap |
An excavated or bunded area in a critical source area or the bed of river that is not continually flowing that is designed and constructed solely for the purpose of allowing sediment to drop from the water column. |
Site-specific river flow |
The flow that must be maintained below a surface water take point. |
Solid animal effluent |
Solid excreta from land-based animals that cannot be pumped and sprayed, including bedding material and manure, but does not include dead animals or animal parts. |
Stockholding area |
It has the same meaning as in the National Environmental Standards for Freshwater 2020: (a) an area for holding cattle at a density that means pasture or other vegetative ground cover cannot be maintained (for example, feed pads, winter pads, standoff pads, and loafing pads); but (b) does not include an area used for pastoral purposes that is in the nature of a stockyard, milking shed, wintering barn, or sacrifice paddock. |
Stormwater network |
An interconnected system of pipes, open channels, treatment devices and ancillary structures which are operated by a territorial authority, network utility operator, company or collective and used for collecting, conveying, diverting, storing, treating, or discharging stormwater. |
Stormwater sub-catchment |
An area of land defined for the purposes of managing the quantity and quality of stormwater. |
Taiāpure |
A coastal fishing area of special significance to iwi. |
Taoka/Wāhi taoka |
A treasured place or valued possession. |
Te Mana o te Wai |
Te Mana o te Wai - the vital importance and health of our water - is a national policy emphasising that the health of our waterways must come first, above all else. |
Vertebrate toxic agent |
A trade name product used to control, kill, or limit the viability of vertebrate pests (such as rabbits, possums, and rodents), including products that have a negative effect on reproduction but do not include attractant or repellent substances that are not toxic. |
Wāhi tūpuna |
Landscapes and places that embody the relationship of mana whenua and their culture and traditions with their ancestral lands, water, sites, wāhi tapu and other taoka. |
Waste |
Has the same meaning as in the Waste Minimisation Act 2008 as set out below: (a) means anything disposed of or discarded; and (b) includes a type of waste that is defined by its composition or source (for example, organic waste, electronic waste, or construction and demolition waste); and (c) to avoid doubt, includes any component or element of diverted material, if the component or element is disposed of or discarded |
Waste oil |
Any oil that has been refined from crude oil, or any synthetic hydrocarbon oil, that has been used, and as a result of such use, has become unsuitable for its original purpose due to the presence of impurities or contaminants or the loss of original properties. |
Weir |
An open-topped structure across the full width of any lake or river that: (a) alters the water level and the flow characteristics of the water; and (b) allows water to flow passively through or over top. |