Please note, ORC uses the Kāi Tahu spelling of Manuherekia.
We are developing a Land and Water Regional Plan (LWRP) in partnership with Kāi Tahu whānui, and with feedback from the greater Otago community.
Join the kōrero on the proposed direction of the Plan to care for Otago's lakes, rivers and streams and guide the activities that impact them.
We have a summary of proposed new rules and regulations that we encourage you to look over.
The Manuherekia Rohe community is one of the first we worked with to develop a preferred approach to water and land management. We prioritised this area (along with the Arrow and Cardrona catchments) because it had many expiring deemed permits and policy work had already been done.
Work between the community and ORC started in 2019, with a key partner being the Manuherekia Reference Group, a range of stakeholders that ORC meets with monthly. The reference group represents the wide-ranging interests of the community and helped us develop options for water flow management, which are now being discussed with the wider community (details below).
You can view a summary report of the submissions, as well as the full set of submissions below.
Media release - Summary report on Manuherekia Management Scenarios consultation
May 2021 Manuherekia Management Scenarios consultation document.
Manuherekia Scenarios Consultation report
The preferred approach will be drafted into the Manuherekia Rohe chapter of the proposed Land and Water Regional Plan.
The new plan will be notified late 2024. Once this plan is notified, you can make a submission saying what you like or how it could be improved.
Under national legislation, regional councils must manage waterways at an appropriate scale for setting freshwater objectives and limits.
We have set five Freshwater Management Units (FMUs) and divided the Clutha Mata-Au FMU into five rohe (areas). One of these is the Manuherekia Rohe, which is based on the catchment area of the Manuherekia River.
The Manuherekia Rohe is combined with the Roxburgh Rohe and the northern part of the Taieri Rohe when considering socio-economic information. These communities have close economic ties – for example, many residents live in one area and work or spend time in the others. The three areas combined are referred to as the ‘Inland’.
In 2018, the area was home to around 13,000 residents (6% of Otago’s population),an increase of 15% from 2006. The economy of this area depends on the water-reliant agriculture sector (which provides for one in five jobs) and tourism-related industries (15% of all jobs). Administrative services (13%) is the third largest sector in the area, with the sub-category of employment services providing 10% of all jobs. Together, these industries account for around half of the employment in the ‘Inland’ area.
It is important to understand Māori history and the Māori economy when developing policy and assessing its impact. Pre-European Māori history shapes today’ Aotearoa, and the Māori economy is integral to the national economic system. ORC is partnering with Aukaha and Te Ao Marama to develop an overview of Kāi Tahu history and economy.
The Manuherekia Rohe sits between the Dunstan Range to the west, the St Bathans Range to the north, the Hawkdun Range and Rough Ridge to the east and the Knobby Range to the South. The Manuherekia River, the rohe’s main water body, flows for 85 km in a south-west direction towards Alexandra where it joins the Clutha Mata-Au River. The rohe stretches over approximately 3,000 km2. The climate of the Manuherekia Rohe is semi-arid, characterised by cold winters, warm, dry summers and low rainfall. The area is dominated by pasture grasslands on the flat and gently sloping land, while tussock grasslands are common in the high country. The lower end of the rohe has the urban area of Alexandra, and the settlements of Omakau and Ophir are small but growing.
Analysis of Manuherikia River Flow Data 2023
Application by Matakanui Station Limited to Take water from Neds Creek
CHES Implementation for the Manuherekia River, Otago
Discharge Gauging Data for the Manuherekia Catchment
ESPC Briefing Paper - Manuherekia Minimum Flow Update
Instream Habitat and Minimum Flow Requirements in the Manuherekia River 2016
Interim Review of the Manuherekia Hydrological Flow Models 2020
Invertebrate Drift Flow Relationships Comparison Between the Manuherekia and Other Rivers 2023
Invertebrate Drift Relationships for the Lower Manuherekia River Memo 2021
Lauder Creek Hydrology Report 2021
Management Flows For Aquatic Ecosystems In The Manuherekia River And Dunstan Creek 2016
Manuherekia Catchment Goldsim Model Scoping Document (Revised Draft) 2020
Manuherekia Catchment Hydrology Joint Expert Statement Revised Draft 2023
Manuherekia Catchment Hydrology Model Report 2022
Manuherekia Hydrology Report 1 2020
Manuherekia Catchment Hydrology Joint Expert Statement Revised Draft 2023
Manuherikia climate change assessment
Manuherikia Fish risk assessment
Manuherekia minimum flow scenario assessments
Manuherikia Hydrology model - calibration
Manuherikia hydrology model - ecology
Manuherikia Hydrology Model - scenarios
Manuherikia Hydrology Model Report
Manuherikia invertebrate drift study
Manuherikia natural character assessment
Manuherikia water quality state and trends
Invertebrate Drift Flow Relationships Comparison Between The Manuherekia And Other Rivers 2023
Thomsons Creek Hydrology Report 2021
Note that the memoranda on the Hydrology Model (Calibration, Ecology and Scenarios) are currently in draft form. The hydrology model and habitat modelling is currently being reviewed.
This summary provides an overview of the provisions relating to the Manuherekia Rohe (area). This includes environmental outcomes, target attribute states and area-specific rules and limits. The rules and limits are in addition to those in the region-wide rules covered in the other summaries.
If you are unsure of any particular terms, there is a glossary of terms.
Overview of content updates:
In its new Land and Water Regional Plan ORC must set environmental outcomes for the freshwater values identified in the Manuherekia Rohe. An environmental outcome statement describes the desired future state that communities in the Manuherekia Rohe and tangata whenua would like to see for a specific value.
The environmental outcome statements are very similar across all FMUs and rohe in Otago, which reflects the fact that the aspirations that tangata whenua and the different communities have for the environment are largely consistent across the region. Table 1 sets out the draft environmental outcomes for the Manuherekia Rohe.
Value |
Environmental Outcomes for Manuherekia rohe |
Attributes to measure and monitor
|
NPSFM compulsory values (apply to every FMU/rohe) |
||
Ecosystem health |
Freshwater bodies support healthy freshwater ecosystems with thriving habitats for a range of indigenous species, and the life stages of those species, that would be expected to occur naturally. |
Rivers: Ammonia Nitrate Suspended fine sediment E. Coli Dissolved reactive phosphorus Periphyton Macroinvertebrates (MCI/ASPM) Fish IBI E. Coli primary contact sites Macroinvertebrates (QMCI) score*¹ Deposited fine sediment* Dissolved oxygen* Ecosystem metabolism* Lakes: Phytoplankton (Chlorophyll-a) Total nitrogen Total phosphorus Ammonia Cyanobacteria* Submerged plants (natives)* Submerged plants (invasive)* Lake-bottom dissolved oxygen* Mid-hypolimnetic dissolved oxygen* |
Human contact |
Water bodies are clean and safe for human contact activities and support the health of people and their connections with water bodies. |
Rivers: E. Coli Suspended fine sediment Periphyton E. Coli primary contact sites Lakes: Phytoplankton (Chlorophyll-a) Cyanobacteria (Biovolume cubic millimetres per litre)* |
Threatened species |
The freshwater habitats of threatened species are protected and support the persistence and recovery of threatened species over time. |
All the attributes listed for Ecosystem Health above. Recency of presence National conservation category and status Regional conservation category and status Number of sub-populations |
Mahika kai (food and resource gathering) |
Mahika kai resources are restored to a condition in which populations of valued mahika kai species are self-sustaining and plentiful enough to support cultural take. Mana whenua are able to safely access, harvest and use these resources now and in the future. |
All the attributes listed for Ecosystem Health above.
|
Other values (apply to every FMU/rohe) |
||
Natural form and character |
Freshwater bodies and their riparian margins, and any connected receiving environment including any estuaries and hāpua (lagoon) are able to behave in a way that reflects their natural form and character to the greatest extent practicable, and the natural form and function of unmodified water bodies is protected. |
Rivers: Suspended fine sediment Periphyton Macroinvertebrates (QMCI) score* Deposited fine sediment* Lakes: Phytoplankton (Chlorophyll-a) Cyanobacteria* Submerged plants (natives)* Submerged plants (invasive)* Lake-bottom dissolved oxygen* Mid-hypolimnetic dissolved oxygen*
|
Drinking water supply |
Provided the health and wellbeing needs of water bodies and freshwater ecosystems are met, source water from water bodies (after treatment) is safe and reliable for the drinking water supply needs of the community. Activities do not introduce or increase the concentration of contaminants in water, so that, after existing treatment, it no longer meets drinking water standards |
|
Wāhi tūpuna (sites of significance to iwi) |
Cultural associations with wāhi tūpuna are maintained, visible, and whānau are able to access, use and relate to wāhi tūpuna now and in the future. |
|
Fishing |
Fish are safe to eat; and Insofar as it is consistent with the protection of indigenous and threatened species, the spawning and juvenile rearing waters for trout and salmon are provided for. |
Rivers: E. Coli Suspended fine sediment Periphyton Nitrate Suspended fine sediment Macroinvertebrates (MCI/ASPM) Fish IBI Macroinvertebrates (QMCI) score* Lakes: Phytoplankton (Chlorophyll-a) Cyanobacteria (Biovolume cubic millimetres per litre)* |
Irrigation, cultivation and production of food and beverages |
Provided the health and wellbeing of water bodies and freshwater ecosystems and human health needs are met, the cultivation and production of food, beverages and fibre is enabled. |
Rivers: Suspended fine sediment Periphyton Water quantity |
Wetlands |
Wetlands are protected, and their ecosystem health, indigenous biodiversity, and hydrological functioning is restored where degraded. |
Rivers: E. Coli Suspended fine sediment Periphyton Nitrate Suspended fine sediment Macroinvertebrates (MCI/ASPM) Fish IBI Macroinvertebrates (QMCI) score* Lakes: Phytoplankton (Chlorophyll-a) Cyanobacteria (Biovolume cubic millimetres per litre)* |
Taoka species (treasured species) |
Thriving, connected habitats for indigenous species are restored and sustained for ever and their mauri is intact. |
|
Values that apply to specific FMU |
||
Commercial and industrial use |
Provided the health and wellbeing of water bodies and freshwater ecosystems and human health needs are met, commercial and industrial activities are enabled. |
Rivers: Suspended fine sediment Periphyton Water quantity |
Hydro-electric power generation |
Existing hydro-electric generation activities are developed, operated, maintained and upgraded in a way that meets the environmental outcomes to the greatest extent practicable. |
|
¹*Asterisk indicates that the baseline state of these compulsory attributes is not known, but monitoring is now being undertaken.
Attributes are indicators that we can measure and monitor. Attributes tell us about the state of a river or lake. A target attribute state (TAS) is the state that an attribute must achieve to make sure that an environmental outcome is met. The timeframe for achieving the TAS for each FMU is set by the environmental outcomes for the FMU. For the Manuherekia Rohe, the environmental outcomes are to be achieved by 2050. By monitoring attributes and comparing their baseline state with their TAS we learn how well how well we are on track towards achieving the environmental outcomes for this rohe.
While the environmental outcome statements are largely consistent across Otago, baseline states and TAS are usually specific to each FMU and rohe. Attributes for each value and baseline states for those attributes have been identified along with trends derived from the Otago Regional Council's State of the Environment (SoE) monitoring data.
The baseline state and TAS for the Manuherekia Rohe are in the map below.
Zoom into an area and view the various locations of proposed monitoring sites in an area(s).
Select the yellow dot representing a proposed monitoring site to see the Target Attribute States.
You can further select the Target Attribute States table to view a larger version of the table.
(Note: If you are on a mobile device, tap on the arrow next to the 'X' icon for the table to show.)
National direction requires Council to set limits as rules or action plans (as appropriate) to achieve the environmental outcomes. This can be done at a region-wide level or at FMU/rohe level. The draft region-wide rules are set out in different briefing papers, including the briefing papers Primary Production, Wastewater, Stormwater, Earthworks, Water Quantity and various others. However, for the Manuherekia Rohe a number of specific rules are proposed that are needed to make sure the environmental outcomes for this rohe are achieved over time. These additional rules, which will be included in the Manuherekia rohe chapter of the new Land and Water Regional Plan, are shown in the table below.
Contaminants of concern |
Draft LWRP |
Rivers Periphyton (TNTP) E. Coli Suspended fine sediment Groundwater Arsenic E. Coli |
|
The Manuherekia Rohe chapter will also include take limits and environmental flows and levels for rivers, lakes and aquifers in this rohe.
Take limits reflect the total quantity of water that can be taken, dammed or diverted from a stream, river, lake or aquifer. Once the combined rate of take for all consented water takes, diversion or damming activities from a water body matches this take limit no further water can be allocated in new consents.
Environmental flows (for rivers or streams) or environmental levels (for lakes and aquifers) include minimum flows or levels that when reached all consented (and some permitted) takes, diversions and damming activities must cease. These restrictions on water taking, diversions or damming activities typically occur during dry periods and are needed to make sure after important values, such as threatened fish, drinking water supply or mahika kai (food and resource gathering) values, are looked after.
Environmental levels and take limits for the lakes and reservoirs in the Manuherekia Rohe are shown in the table below.
Given its uniqueness, it is proposed that a narrative take limit is set for the Blue Lake. This limit will prohibit any new takes, damming or diversions (except for takes that are permitted under the Resource Management Act 1991) that could impact water levels this lake. The prohibition will ensure that this lake will continue to behave in its current state.
Reservoirs in this rohe, such as the Poolburn Dam and the Manorburn Reservoir will be subject to the minimum flow and take limit set for the Manuherekia River catchment.
Name |
Environmental level(s) |
Take limit (litre per second) |
Natural lakes (unmodified) |
||
Blue lake |
Natural minimum water level |
Narrative — no new taking, diversions, damming or discharges from the lake or upper catchment. |
Controlled lakes |
||
Idaburn Dam Lower Manorburn Dam Falls Dam Greenland Reservoir Manorburn Reservoir Moa Creek Reservoir Poolburn Reservoir |
Lake level managed by the minimum flow of the Manuherekia river catchment
|
Subject to the take limit of the Manuherekia river catchment.
|
Bespoke limits and environmental flows will be set in the Land and Water Regional Plan for the Manuherekia River. A staged increase in environmental flows over time has been proposed to achieve ecosystem health for the river. This would be implemented as follows:
Name
|
Environmental flow(s) |
Take limit (l/s) |
Further primary allocation available (estimate based on best available information) |
River catchments managed by bespoke limits | |||
Manuherekia at Campground |
900 l/s (from notification) 1200 l/s (from 2030) 2500 l/s (from 2040) |
Maximum instantaneous rate of take of 32,000 l/s | No |
The draft LWRP contains the following additional provisions related to environmental flows in the Manuherekia:
The Manuherekia rohe contains various aquifers.
For some aquifers that are not hydraulically connected to surface water, such as the Manuherekia Claybound Aquifer and the Ida Valley Groundwater Management Zone, take limits will be set based on a proportion (35%) of the mean annual recharge of that aquifer. National direction also requires Otago Regional Council also to set environmental levels for these aquifers. Because we will not have sufficient groundwater level monitoring data to set environmental levels in the Land and Water Regional Plan when it will be notified, environmental levels for these aquifers will be set at a later date.
For the Manuherekia Alluvium Aquifer, which has a close hydraulic connection to Manuherekia river, any taking of water will be subject to the take limits and environmental flows set for this river.
Name |
Environmental level(s) |
Take limit (volume) |
Aquifers with default limits |
||
Ida Valley Groundwater Management Zone Manuherekia Claybound Aquifer Manuherekia Groundwater Management Zone |
Not required to be included in the new LWRP at this time |
35% mean annual recharge |
Alluvial ribbon aquifers |
||
Manuherekia Alluvium Aquifer |
Groundwater level managed by the river catchment minimum flow |
Subject to river catchment take limit
|
Outstanding water bodies are water bodies that have one or more outstanding values. National direction requires the Otago Regional Council to identify outstanding water bodies and protect their important values. The table below lists the outstanding water bodies in this rohe and describes their outstanding values.
Below is a map featuring all the water bodies in Otago.
You can zoom in and view the various water bodies in an area(s).
Water bodies are shown in a blue colour. Select an area to view the water body name.
(Note: if you are on a mobile device, after selecting a water body, tap on the arrow next to the 'X' icon to view more information.)
Unique identifier |
Site identifier |
Values and characteristics |
Ecology |
||
ECL14 |
Upper Manuherekia |
|
ECL15 |
Hopes Creek |
|
Physical |
||
None identified. |
||
Recreation |
||
None identified. |
||
Natural character |
||
NAT12 |
Hopes Creek |
Active bed
Margin
Context
|
NAT13 |
Manuherekia |
Active bed
Margin
Context
|
NAT14 |
St Bathans |
Active bed
Margin
Context
|
Natural features and landscapes |
||
LAN38 |
Manorburn and Greenland Reservoirs |
|
LAN39 |
Poolburn Reservoir |
|
LAN40 |
Upper Lauder Creek |
|
LAN41 |
Upper Dunstan Creek |
|
LAN42 |
Upper Manuherekia |
|
LAN43 |
Poolburn Gorge |
|
LAN44 |
Ophir Gorge |
|
Contact your rohe's Catchment Advisor for advice and assistance on sustainable land management practices that protect Otago’s waterways.
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