Hurunui-Waiau Zone Committee HURUNUI-WAIAU ZONE COMMITTEE ... · 11.12.2017 · Hurunui-Waiau Zone...
Transcript of Hurunui-Waiau Zone Committee HURUNUI-WAIAU ZONE COMMITTEE ... · 11.12.2017 · Hurunui-Waiau Zone...
Hurunui-Waiau Zone Committee
A g e n d a
3.00pm, Monday, 11 December 2017 10am – Zone Committee Field Trip
12.30 – Biodiversity Working Group Workshop
1.15pm – Zone Committee Only Briefing Workshop
Cheviot Community Centre, 3 Caverhill Road, Cheviot
Community Partnership in Growth and Wellbeing
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Committee Membership: John Faulkner (Chairperson) Mayor Winton Dalley (Hurunui District Council) Cr Vince Daly (Hurunui District Council) Cr Cynthia Roberts (Canterbury Regional Council) James Costello Ben Ensor (Deputy Chairperson) Michele Hawke Ken Hughey James McCone Makarini Rupene (Te Ngāi Tūāhuriri Rūnanga) Dan Shand Representative to be advised (Te Rūnanga o Kaikōura)
Quorum:
The quorum of the meeting consists of:
• half of the members if the number of members (including vacancies) is even; or
• a majority of members if the number of members (including vacancies) is odd.
Committee Secretary – Michelle Stanley
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The purpose of local government:
(1) The purpose of local government is— (a) to enable democratic local decision‐making and
action by, and on behalf of, communities; and (b) to meet the current and future needs of communities
for good‐quality local infrastructure, local public services, and performance of regulatory functions in a way that is most cost‐effective for households and businesses.
(2) In this Act, good‐quality, in relation to local infrastructure, local public services, and performance of regulatory functions, means infrastructure, services, and performance that are — (a) efficient; and (b) effective; and (c) appropriate to present and anticipated future
circumstances.
(Local Government Act 2002 – Amendment Act 2012)
HURUNUI – WAIAU ZONE COMMITTEE
WORKSHOP & MEETING
Monday, 11 December 2017,
Cheviot Community Hall, Cheviot
10.00am Zone Committee field trip – mahinga kai and farm practices (Parnassus)
12.30pm Zone Committee lunch (Cheviot)
12.30pm – 1.15pm Biodiversity subcommittee working lunch (Cheviot)
1.15pm – 2.45pm Committee‐only briefing workshop
AGENDA 3.00pm Zone Committee Meeting commences with karakia and formal order of business
Apologies
Announced urgent business
Interests register (changes or updates)
Confirmation of minutes – 20 November 2017
Matters arising
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1 3.15pm Confirmed meeting schedule 2018 Ian Whitehouse and Michelle Stanley
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2 3.15pm Zone Committee Workshops and Briefings Michelle Stanley and Graham Sutherland, Hurunui District Council
18‐20
3 3.20pm Update on Regional Committee Winton Dalley and Michele Hawke
4 3.25pm Update from Zone Committee members on activities and meetings attended that relate to the Committee’s outcomes for the zone
5 3.30pm Public Contribution
6 3.35pm Update organisations wishing to speak
7 3.40pm Update from Zone Delivery including St Anne’s Lagoon Leanne Lye, Environment Canterbury
21‐33
8 4.00pm Proposed region‐wide approach to resolving issues with river‐bed lines (paper to be tabled)
Environment Canterbury
4.20pm BREAK
9 4.40pm Initial results from research into potential impact of permitting dryland farming Josh Brown, Hurunui District Landcare Group
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10 5.10pm Establishing a subcommittee to progress discussions with AIC on further deferring a consent review in relation to HWRRP minimum flows Ian Whitehouse, Environment Canterbury
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11 5.35pm Additional technical information relating to consideration of deferring a review of water take consents:
i. Advice on whether implementing HWRRP minimum flows could be deferred on consents currently being renewed. Lisa Jenkins, Environment Canterbury
ii. On‐farm impacts of irrigation restrictions Peter Brown and Andrew Barton, AIC
iii. Comparison of reliability of supply for irrigation schemes in Canterbury (paper to be tabled) Jeanine Topelen, Environment Canterbury;
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12 6.10pm Wilding conifer strategy and action in the zone Alan Tinnelly, MPI
66‐68
13 6.25pm Zone Facilitator’s report Ian Whitehouse, Environment Canterbury
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6.30pm Meeting concludes
Register of Interests for the Hurunui‐Waiau Zone Committee
Committee Member Interests
James Costello Farm owner – sheep in the Hurunui Catchment
Water Resource Consent to take water from the Waitohi River
Shareholder in Hurunui Water Project
Possibly an affected landowner by infrastructure of Hurunui Water Project
Dryland Farmers Committee member
Ben Ensor Land owner in the coastal hills, Jed and lower Waiau catchments.
Managing director of Seaward Stock Company Ltd, comprising sheep, beef and cropping enterprises.
Consent holder to take water for irrigation from a stream hydraulically connected to the Waiau River.
Member of the Hurunui Waiau Landcare Group (Dryland Farmers Group).
John Faulkner Dairy farm owner in the Amuri Basin.
Irrigation water supplied by Amuri Irrigation Company Ltd (Shareholder).
Dairy Support block owner, consent to take water from a gallery.
Member of the independent irrigators Group.
Michele Hawke Nil
Dan Shand Land owner Hurunui and Waiau catchments
Dry land farmer
Member of the Hurunui/Waiau Landcare Group
Mayor Winton Dalley Register of Interests lies with the CEO of the Hurunui District Council.
Ken Hughey Professor of Environmental Management, Lincoln University (2 days per week)
Chief Science Advisor, Department of Conservation, Wellington (3 days per week)
Board member Waihora Ellesmere Trust
Board member Hanmer Springs Conservation Trust
Member Royal Forest and Bird Protection Society.
Member Royal Society of NZ
Member NZ Geographical Society.
Occasional contract water‐related research work including for Environment Canterbury.
Makarini Rupene TBC
James McCone Dry Creek Dairy Ltd‐ AIC Balmoral scheme
Kinloch Dairy Ltd‐ AIC Waiau Scheme
Amuri Irrigation Company Director
Committee Member Upper Waiau Independent Irrigators
Informal interest in potential emu plains irrigation
Councillor Vince Daly Farm owner ‐ mixed cropping and livestock farm
Water resource consent to take water from unnamed lake in Jed catchment
Cynthia Roberts Register of Interests is held by Environment Canterbury.
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Meeting Hurunui‐Waiau Zone Committee
Date and Time 20 November 2017, 3.00pm
Venue Waiau Community Hall, Waiau
Agenda http://www.hurunui.govt.nz/assets/Uploads/20‐November‐2017‐HWZC‐Agenda‐WEB.pdf
Members Present John Faulkner (Chair), Mayor Winton Dalley, Cr Vince Daly, Cr Cynthia Roberts, James Costello, Ben Ensor, Michele Hawke, Ken Hughey, James McCone, and Dan Shand.
In Attendance Environment Canterbury (ECan) – Ian Whitehouse (Zone Facilitator), Michael Bennett, Leanne Lye, Andrew Parrish, Lisa Jenkins, Stephen Bragg, Ned Norton, Caroline Hart, Hamish Graham, Jeanine Topelen and Peter Taylor
Amuri Irrigation – Andrew Barton, David Croft
Cheviot Irrigators Group – Robb MacBeth
Hurunui Water Project – Christina Robb and Chris Pile
Emu Plains irrigators – Brian Ellwood
Fish and Game New Zealand – Scott Pearson.
Hurunui District Council – Cr Nicky Anderson
Rainer Irrigation – Neville Brightwell.
Rural Advocacy Network – Jamie McFadden
Te Rūnanga o Ngāi Tahu (TRONT) – Lisa Mackenzie and Matt Dale
Ryder Consultants – Gavin Kemble and Greg Ryder
Committee Secretary – Michelle Stanley.
Recording Device A recording device was in use for the accuracy of the minutes.
Karakia Stephen Bragg led the Karakia.
Apologies Apologies were received from Makarini Rupene.
THAT THE APOLOGIES BE ACCEPTED.
Faulkner/Costello CARRIED
Conflict of Interest Declarations
James McCone to forward to Michelle Stanley, Secretary, a change to the Interests Register.
Urgent Business Nil.
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Minutes THAT THE MINUTES OF THE COMMITTEE MEETING HELD ON 16 OCTOBER 2017 ARE CONFIRMED, SUBJECT TO THE FOLLOWING AMENDMENTS:
Page 5, Members Present, Change ‘Chair’ to Ben Ensor.
Page 5, In Attendance, include Matt Dale in Te Rūnanga o Ngāi Tahu (TRONT). And exclude Lesley Shand from the minutes now and for all other meetings.
Page 7, second to last bullet point, change reference to Rural Advocacy Group to Landowner.
Page 8, Item 1, third bullet point, change to read “…but not directly into the target river system.”
Page 9, Item 4, change to Amuri Irrigation Company. (misspelling).
Page 9, item 2, change to read: “ECan had advised that they were working on their Long Term Plan and that the CWMS and biodiversity were their highest priorities in the Long Term Plan.” to replace “The emphasis is on the Long Term Plan process at this stage. The CWMS process, biodiversity and Biosecurity were discussed.”
Page 10, Item 6, change heading to “technical evaluation of…”
Page 10, Item 6, fourth bullet point, change ‘rational’ to ‘rationale’.
Page 11, Item 6, fifth bullet point, change to read: “A query was raised on the possibility of delaying the renewal date of the Phoebe Plains consent due to linkage with improving the flows in St. Anne’s Lagoon. They will be affected by the new minimum flow rules.”
Page 12, second bullet point, change ‘complied’ to ‘compiled’.
Page 12, third bullet point, change to “it was queried as to why Waiau needs storage when the new reliability would be similar to the current Balmoral reliability.”
Faulkner/Costello CARRIED
Matters Arising:
Matters Arising – Item 8, Braided River Biodiversity Management (page 6)
Ken Hughey tabled a document outlining the general conditions related to the HWP consent condition to implement a Trust.
As the Trust has not yet been established, there are no foreseeable issues to extending the mandate and scope of the Trust to cover the interests of all the Hurunui irrigation companies, like HWP, AIC, Ngai Tahu Property and, if water does go into the Waipara River from the Hurunui River, the Waiau River and Waipara Rivers as well.
Ken noted that the Biodiversity flagship program is very similar to what was envisaged to be the purpose of the HWP Trust.
It was decided that members would read through the information and come prepared for discussion at a future meeting.
Ken to report back with a step‐by‐step plan on achieving this.
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Item 2, Update from Zone Committee members (page 9)
John Faulkner and Mayor Winton Dalley have been to visit David Bedford and reported that he is open to visitors now if anyone wishes to visit.
Ian Whitehouse delivered all the notes and cards to him.
Item 9, Input to Environment Canterbury (page 13)
Ken Hughey will follow up on the swimming opportunities.
Zone Facilitators Report ‐ Initiatives (Page 14)
Ken Hughey to follow up on the before and after photos about the Hurunui Conservation Trust Wetlands Project.
Zone Facilitators Report – Proposed further water quality (E.coli) monitoring (Page 15)
Ned Norton and Ken Hughey had a meeting last week and they are both happy with the outcome. It is still a work in progress and ECan have had two trips to the River since that meeting. Staff are working to pinpoint exactly where the sources of E. coli are.
Item 4, Update from HDLG and other organisations (Page 10)
It was reported that four FEP auditors attended the training day run by AIC.
Discussions at the training day were held around how the audit process goes beyond what they are required to do. An auditor will assess far more than the required checklist and will make suggestions to a farmer that they are not obliged to do, but will help them to function better.
There will be another field day in the Autumn on this topic.
Correspondence John Faulkner tabled a memo received from Philip Burge, Principal Consents Advisor ECan, on the ‘Number of Land Use consents related to riverbeds and their margins in the Hurunui‐Waiau Canterbury Water Management Strategy zones’. A total of 44 applications are recorded as being received and decided since 11 August 2012. All decided applications were granted on a non‐notified basis. This does not include applications currently in process.
The applications of decided land use consent applications related to flood protection, structures, stock grazing and clearance of riverbed and riparian vegetation in riverbeds and riparian zones, in the Hurunui‐Waiau CWMS Zone, (excluding gravel extraction and bores).
Letter from ECan regarding Riverbed Lines
The letter was taken as read. Discussion was held on the ECan’s return letter. The following was noted:
It was felt that this reply was predictable.
It was commented that what ECan are proposing to do is good but not fast enough.
Bill Bayfield, ECan CEO, has committed to coming back to the Committee in December with their proposed process for resolving the riverbed line issue across Canterbury including specific work in the Hurunui‐Waiau. It was noted that Bill Bayfield attended the zone
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committee only workshop before the October Zone Committee meeting. It was noticed by the public gallery that he did not stay for the Public Meeting.
The Zone Committee made it clear that they are not happy with the response to its letter and the timeframe given for resolution of the riverbed issue.
Jamie McFadden reiterated that whilst this discussion is happening, the mapping is still continuing as is the issue of the how that information is being used. He would like those databases to be removed as the validity of the gathered information is in question.
Jamie McFadden said that while assurance from ECan that those techniques of entering landowners properties without permission has been stopped, this is still happening. It is requested that any evidence of this occurring be forwarded onto the Zone Committee to act upon accordingly.
Proposed Meeting Schedule 2018
The 2018 proposed meeting schedule was considered. Discussion was held around the venues through winter. It was requested that the Committee Secretary and Ian Whitehouse relook at the venues and come back to the Zone Committee with some warmer venues through the colder months of the year.
Ian Whitehouse to send out invitations to the meetings and workshops.
1. Update on Regional Committee
No update was given due to there being no scheduled meeting since the last Zone Committee meeting.
2. Update from Zone Committee members on other activities and meetings attended that relate to the Committee’s outcomes for the Zone.
Cr Cynthia Roberts attended the Kaikōura Commemorate Ceremony and opening of the marina. She noted that it was a great and thoughtful ceremony.
The Pest Management Plan review is in the final stages and is on the website. The submission process has closed but it is still open for technical input. It is shaping up to be a very good plan.
It was noted that many submissions were submitted to the Plan. Mayor Winton Dalley felt that there was not a lot of consideration given to submissions on the counterproductive lack of cost sharing especially incentivising landowners to follow the Plan.
Turi McFarlane and has been awarded a Nuffield scholarship and will be studying Ecosystem services and various international agricultural systems and how they can be applied to the New Zealand system. This is great for Turi but also for Hurunui as he is a big part of the Hurunui District Landcare Group.
Mayor Winton Dalley spoke to the media on the ECan announcement to the swimming quality downgrade on the Hurunui River. He was asked to respond to the announcement to which he responded that according to the discussions that the Hurunui Waiau Zone Committee have had, the grade is likely due to the natural sources of E.Coli up‐stream and until there is some certainty around the source of the E.Coli, then there is not a lot that can be reported.
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3. General Public Contribution
The Zone Committee notes the handout on issues of water and pollution by WADE, from a member of the public. To be taken and read.
REPORTS, SPEAKERS AND PRESENTATIONS
4. Update from Hurunui District Landcare Group, HWP and any other organisations wishing to speak
Chris Pile, HWP, noted that HWP have two major resource consents in progress. The first one is the nutrient discharge consent for the Waipara catchment which has been lodged. He noted the discharge consent application is to quantify the load that HWP is already entitled to, as part of their previous consent to take irrigation off a farm, but as that part of the plan changed between the original consent and currently, it is no longer a permitted activity so needs clarification to give farmers certainty to invest.
The other consent, which is yet to be applied for, is for the on‐plains storage that is proposed for the north side of the Hurunui River. They are working together with Ngāi Tahu and Amuri Irrigation to build a facility on the Ngāi Tahu Balmoral Forestry in the north west corner. They are estimating that the consent application will be submitted early 2018.
A member of the public asked what had been looked into regarding crossing the Mandamus and understood that it was not acceptable at the Glenrae storage. John Faulkner clarified that a presentation was given a few meetings ago on the options for storage. This was a hypothesised scenario and it was noted that the Glenrae storage option, whilst the most attractive, would require a Plan change so unlikely to happen.
Hurunui District Landcare Group are still working on the dryland farming research and are on track to present it to the December Zone Committee meeting.
AIC, Andrew reported that the piping project is finished and successful. Quite a few farmers are enjoying the quietness of the new gravity driven centre pivot system rather than the whirring of a pump.
Works are progressing in other areas namely the Waireka Scheme, which is a small 400 hectare border dyke scheme. They are putting in a pipe beside the open race as part of a process to change from border to spray irrigation in a manner that gives the farmers the lead in the process. This is the focus for next year.
5. Progress Report on Zone Delivery Leanne Lye, ECan
Leanne Lye spoke on the progress of the zone delivery team. The following was noted:
Michael Bennett will be spending approximately thirty percent of his time working in the earthquake recovery project team led by Beef and Lamb New Zealand.
The Zone Team are adopting a programme of focussed monitoring on high priority consents in line with regional programme. High‐risk consents/consent holders have been/will be identified and assigned an individual monitoring plan. A small number of farmers who need
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consents in the Waipara and Conway catchments have also been spoken to and are being assisted through the process.
There has been a ‘farming at GMP’ campaign targeting farmers that are not in a collective. These farmers have been contacted and are being supported.
Quarterly meetings with industry and environmental groups have been scheduled for December.
124 consents were monitored in the last quarter and 89 have complied.
AIC, CIG and HDLG are instrumental in ensuring that farmers are operating at GMP.
Immediate steps Biodiversity funding for Lansdowne Farm in Waipara has been signed off.
It was requested that when communication regarding the Hurunui‐Waiau Zone is put into the media, a link/notification is sent to the Hurunui‐Waiau Zone Committee.
The Waiau River at Waiau township has been given a grade of ‘good’ for contact recreation. This is the first time that the new site on the main channel at Waiau township has been given a grade as several years of monitoring are needed before a site is graded.
The Zone Team need to identify at least two projects to enhance Mahinga kai in the zone. It was agreed that the St Annes Lagoon is a good project for this. It was acknowledged that Robb Macbeth, Phoebe Irrigation, has been instrumental in looking at an options for keeping the water in this lagoon in dry years and Robb indicated that they would still be willing to help in the future.
Discussion around how to fix the St Annes issue was held. Leanne Lye to come back to a future meeting with some more detailed information on the issue and possible long term solutions.
This report to include Jeanine’s high‐level feasibility study modelling looking at storage, precipitation and evaporation data to sustain ecological health. Also to include funding options, source of the water and issues of mixing water.
Discussion was held around modelling the excavation that Cr Vince Daly had done at his farm pond and whether a hole could be excavated at St Annes. It was discussed and supported by Hamish, Hydrologist, that the sediment at St Annes Lagoon will not support digging out a deeper hole for the eels as it is quite silty and a hole would fill back in. A suggestion was made that Cr Vince Daly’s pond is looked at via a site visit.
It was agreed that the St Annes Lagoon become the Zone Teams next Mahinga kai project.
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6. Cost of on‐farm water storage or other mitigating strategies to offset increase in minimum flow.
6a. Cheviot Irrigators – On‐Farm Cost to Offset Increases in Minimum Flow Robb Macbeth, Cheviot Irrigators Group
Robb Macbeth spoke to the Zone Committee on the cost of on‐farm water storage and other mitigating strategies to offset increase in minimum flow. He noted that his presentation was a simplistic analysis of the new minimum flow impact and the modelling is based on Phoebe Plains.
He concluded that on‐farm storage is unlikely to be an economical option and farmers would struggle to receive funding to build on‐farm storage. Community storage could potentially be more economic but would be difficult to consent, difficult to fund and many years away. Seasons with significant irrigation restrictions will have a significant impact on profitability. The environmental impact of farming system change is difficult to quantify and requires further work.
Discussion was held and the following was noted:
AIC and CIG are working broadly together but do not see any integration options for storage at this stage. It was asked if CIG see the deferment of minimum flows as a way to encourage integration between CIG, AIC, HWP and Emu Plains. There is potential for this to happen but the issue at the present time is that CIG farmers are right in the midst of the consent renewal process as there are a number of consents due for renewal in the next 12 to 18 months and the new consents will have the new minimum flows. CIG felt that, simplistically, if the new minimum flows were deferred they would have more time and more investment capability to progress an integrated storage solution.
Whilst the Zone Committee are aware that this is just a brief summary it was noted that more data on reliability would lead to a more informed discussion.
Discussion on deferring the consent process to allow time to work on an integrated storage system was held. Andrew Parrish stated that a time‐period cannot be extended/changed on a consent and would require a Plan change to do so. It was suggested that a consent is granted with the existing minimum flows but this then inhibits the health of the river and the moving to minimum flows.
It was reminded that it has always been the Zone Committees view that there would be no minimum flow increase until storage is achieved. If the Committee is still determined to work on and give opportunities for integrated storage then it needs to be careful to not force an individual consent holder into an expensive process to take care of their own storage when there will quite likely be a community storage option coming.
Andrew Parrish and Lisa Jenkins to look into options that would encourage a pragmatic short‐term solution and report back to the Committee on the results.
It was suggested that ECan do some cross referencing between the on‐farm costs presented and the evidence presented to the HWRRP Hearing, as the profit losses presented in the Plan hearings seem lower
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than the costs reported by Phoebe Plains. AIC noted that they are still looking to provide information on the impact of reliability of supply on farm cost from the 2014/2015 season.
Would like more farm specific information to give the Zone Committee a greater degree of comfort. Andrew Parrish to report on this at a future meeting.
Scott Pearson proposed that Fish and Game New Zealand would be interested in funding an alternative farm model over a five year time period. This would be looking at different reliability of supply on irrigated dairy farming systems comparing the current farming model with an alternative farming model on the same farm
This model is already in place in a number of other farms in New Zealand therefore it was felt that there would be no reduction in profitability for a farmer who would choose to trial Fish and Game’s alternative model. Scott Pearson suggested bringing in a farm model expert in to explain it further.
The Zone Committee were in favour of finding out more about this offer.
Discussion was held around the worry that what was being discussed was more around efficiency rather than reliability. Whilst it is certain that farms will increasingly become more water efficient, this does not fix the reliability of water flows in a dry season. If a farm becomes more efficient in its practices and subsequently decides to relinquish the unneeded water take from its consent to save paying for it every year, then it will still have the same issues with reliability in a dry period under minimum flow restrictions.
Andrew Parrish noted that there are currently plan change processes underway in the OTOP Zone and the Waimakariri Zone and there will be some technical information from these on reliability of supply of other irrigation schemes. He will ask staff to bring the results to the Zone Committee.
6b. AIC’s proposal for more action to improve water quality and biodiversity
Andrew Barton, AIC
Andrew Barton presented to the Committee on AIC’s proposal for more actions to improve water quality and biodiversity.
Andrew spoke on the background of AIC. AIC proposed to deliver ASM and FEPs across irrigators and the Zone Committee recommended that ECan delay consent reviews which ECan adopted. Minimum flow increases will have an economic impact on AIC and its shareholders and storage comes at a significant cost, focus and resources. They feel that better outcomes can be achieved by further delaying consent reviews.
They are focusing on the fish screen review, hapua monitoring, mid‐river jetboat access, riverbed bird habitat, mahinga kai outcomes on farms exploration, understanding how to improve braided rivers through farming practices, periphyton and water quality monitoring, managed aquifer recharge, project management potential, and storage options.
AIC farmers have improved Pahau River water quality and AIC has met the FEP and audit targets previously agreed to.
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AIC’s next steps will be to get Zone Committee feedback, appointing a project manager, a consultation process and finally a formal proposal to be submitted to the Zone Committee.
Discussion was held and the following was noted:
AIC will not be pursuing a constructed/enhanced wetland in the lower reaches of St Leonard’s Drain due to the high cost and an unwilling seller and therefore will be looking at tributary pumping.
Michael Bennett spoke on some of the trial work of the Kaikoura plains recovery project that could be worth looking at.
It was noted that the report supplied by AIC was modelled on the take utilising the consents that AIC hold. Eventually that saved water would be utilised for example Emu Plains Irrigators would be able to use the extra A allocated water instead of having to put in on‐plains storage.
Andrew agreed that independent irrigators in the lower Hurunui River, whose restrictions are based on the flows monitored at State Highway 1, might not be very happy to know that the river will be half a cumec lower in the middle of the summer. He felt that their reliability would still be superior than anyone who had minimum flows based on the flows recorded at the Mandamus site.
Andrew noted that AIC wish to speak to the affected landowners before coming to the Zone Committee with numbers and a benefit vs impact analysis to see if the nitrate‐nitrogen concentration decrease at State Highway 1 would be worth the decrease in reliability during minimum flows. AIC felt that the decrease in reliability would be small being only 1‐2% and would still be higher than the reliability on the Waiau River.
Andrew noted that they are trying to reduce the concentration of nitrate‐Nitrogen at State Highway 1 by pumping nitrate‐rich water from St Leonard’s Drain. To do that they would need to delink the Pahau Drain and St Leonards Drain’s minimum flows from the main stem minimum flow.
In the approach being proposed, AIC would not pump water in a major flood as this would have a minute effect of nitrate‐nitrogen reduction. They noted that it would be more beneficial to the river to pump in the recession of a flood.
There is an opportunity cost on the water that is not being used plus the price of pumping.
A lot of the shareholders also subscribe to Amuri shares in order to protect themselves against reliability.
They have a consent to take water from St Leonards Drain and do not have to drop water back into the St Leonards but they do.
AIC asked if the River was better off having more water in it with higher nitrate concentrations or lower water flow with less nitrate concentrations. It was agreed that in the short term it was better to have more water in the drain and that AIC’s pumping would improve the health of St Leonards Drain.
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AIC is doing some investigation into the reasons why nitrogen levels are so high in the St Leonards Drain. It is a work in progress.
It was noted that there is some confusion around what AIC thought ECan was offering in terms of support for AIC’s desire for a plan change to enable water storage in Zone B. Clarification was needed.
Zone Committee members expressed its frustration with the continued discussion of storage options without any on ground action and no integrated solution originally requested by the Zone Committee. AIC said they have put all of the plans and paperwork in place but are hindered by the Plan which does not allow storage in Zone B . AIC are committed to putting storage in.
There is a concern that maintaining the current minimum flows will have a detrimental effect to the health of the river. The Committee agreed that the minimum flows must increase sooner rather than later (i.e. implement the HWRRP minimum flows).
A member of the public reminded the Committee of some of the gains that have been made with Farm Environment Plans and Good Management Practice and that it is not all about storage.
It was noted that the Zone Committee has not yet received information from developers supporting a plan to enable major storage in Zone B and so could not assess if this was something that should be part of the plan changes to be notified in mid 2017.
The Zone Committee thanked Andrew for presenting and agreed that there is still more discussion to be held on this topic of deferring minimum flows and storage options.
Break The meeting adjourned for a break at 5.00 pm and reconvened at 5.05 pm.
7. AIC’s approach to Nitrogen Accounting Peter Brown, AIC
Taken as read.
Please email any questions through to Ian Whitehouse.
8. Progress on Technical Matters
8a. Dryland Farming related information
Ned Norton
Ned Norton spoke briefly on the Technical Progress update on Dryland farming related information and the deferral of water takes review issue. He took the information as read and spoke to a presentation that is briefly outlined below:
Dryland Farming related information
1) Work by the Hurunui District Landcare Group is progressing with plans to present to the December Zone Committee meeting. This work will inform what is normal dryland development and typical nutrient increases expected from that.
2) Estimating the potential for dryland forage cropping. A GIS approach has been used to provide an “upper bound” estimate of the area that could be used for winter grazing on fodder crops. This upper estimate needs to be refined by considering climatic and other factors that limit the actual area of winter grazing on fodder crops.
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3) Sources of “manageable” phosphorus loss. Available information, while uncertain, provides a level of comfort that gains from the most manageable sources of phosphorus loss could help to achieve catchment phosphorus limits while permitting “normal dryland development”.
To be discussed more at a further meeting when further information is available.
8b Assessment of likely impact of climate change on the assessment of environmental values at risk if minimum‐flow consent review is deferred.
Suzanne Gabities and Jeanine Topelen, ECan
1) The report was taken as read and the Zone Committee were accepting of the information. The key finding was that taking into account the impacts of climate change, the environmental effects of delaying implementation of HWRRP minimum flows are expected to be similar or slightly worse in the next 15 years compared with the assessment presented last month.
Deferral of water takes review – outstanding questions
2) The Cawthron flow‐setting research adds to the existing basket of assessment tools. If used as part of a full review of HWRRP minimum flows today, would likely result in biophysical assessment that higher flows would increase carrying capacity for trout. Process then subject to all usual consideration of implication s across all values.
9. Updated Zone Committee work Programme
The updated work programme was taken as read. It was noted that the Zone Committee might need to have another meeting at some stage to work on the deferred minimum flows issue. This is not a set work programme and can evolve as needed.
THAT THE ZONE COMMITTEE ACKNOWLEDGE THE 2018 WORK PROGRAMME.
Hughey/Ensor CARRIED
10. Early draft Zone Committee’s 2017 Annual Report
The Early draft of the Zone Committee’s 2017 Annual Report was discussed. The following changes and additions were suggested:
It was suggested that the Ngāi Tahu trial plots of apricots, apples and hazelnuts down by the milk factory would be a great addition. Ian Whitehouse to follow up on this.
key Achievements
o Water on Balmoral
o The Zone Committee is still working regularly tackling the big issues. Relationships are stronger than 12 months ago and there are good constructive working relationships with all the groups.
o The Ministry for Primary Industries fund for earthquake
o Emu Plains lodged their consent, raised some capital and are an incorporated society. Ian Whitehouse to include.
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Recreational ‐ Waiau River has been graded ‘Good’ for swimming. It was noted that the testing site was shifted to a new site on the Waiau River. It was suggested that it would be worthwhile shifting the testing site on the Hurunui River as well.
Ongoing Challenges – this heading was a suggested addition where it would encourage transparency and honest reporting. Email Ian Whitehouse with any issues.
Ken Hughey to send some suggestions.
Opportunities – Auditing numbers from AIC.
Michael Bennett to give Ian Whitehouse some information on the earthquake statistics and achievements in that space.
The impact of Immediate Steps funded project illustrated with pictures. Do some before and after. If have images please send them through.
Braided river issue. Michele Hawke to send some words on braided rivers to Ian Whitehouse.
Amuri Irrigation Company Piping Project (page 2) – change second paragraph to read “it is estimated previously that about 30% of the water was lost from the open races.”
Zone Committee Membership 2017 (page 4) – change to read “Dr Cynthia Roberts (Environment Canterbury, Councillor)”
It was noted that the website which the annual report is on gets a good number of hits and is well read. There are a large number that also ask for a print out of it as well.
It was suggested that in the future it might be good to publicise the Zone Committees KPIs each year.
Urgent Business Nil
Meeting concluded
The meeting concluded at 6.38pm.
Next meeting 11 December 2018 – Cheviot.
16
AGENDA ITEM NO: 1
SUBJECT MATTER:
2018 meeting schedule
REPORT TO:
Hurunui‐Waiau Zone Committee
DATE OF MEETING:
11 December 2017
PREPARED BY:
Ian Whitehouse and Michelle Stanley
ACTION:
For information
2018 HWZC meeting schedule
Following discussion at the November meeting over concerns about the winter venues for the zone
committee’s meetings the 2018 meeting schedule is:
19 February Cheviot
19 March Waikari Hall
26 March Amberley (if required)
16 April Culverden
21 May Greta Valley
18 June Balcairn Hall
16 July Amberley
20 August Amberley
17 September Rotherham
15 October Hawarden
19 November Waiau
10 December Amberley
17
AGENDA ITEM NO: 2 SUBJECT MATTER:
Zone Committee Workshops and Briefings
REPORT BY: Michelle Stanley and Graham Sutherland, Hurunui District Council Secretaries
DATE OF MEETING: 11 December 2017
Action required
Zone Committee members note the information and agree to the recommended approach below with respect to the conduct and management of Zone Committee workshops:
a) That preceding a scheduled workshop, an item be included in the agenda whereby the
Zone Committee recommend the workshop or briefing be open to the public or not.
b) Where possible, the explanation of an upcoming workshop or briefing be included in the previous month’s meeting agenda.
c) Workshops have sometimes been held to enable the Zone Committee to debate issues without the inclusion of public contribution. It may be helpful to permit public attendance at workshops or briefings, however the privilege of public contribution may not be extended in the workshop or briefings where the public is permitted to attend.
d) Any workshop/briefing prior to a public meeting is briefly summarised by the Chair as a regular agenda item.
e) Confidential information from workshops or briefings is not shared publicly.
f) A record is provided at the conclusion of settling on a position, that the position was supported by the workshop or briefing.
Background
Members‐only or “Public excluded” workshops The Zone Committee has recently held members‐only workshops (referred to as “public excluded” on the agenda coversheet) prior to its normal public meetings. This has led to some comment from the public about the use of workshops and meeting processes. This report discusses the rules and obligations of the Hurunui‐Waiau Zone Committee as a joint committee of ECan and the Hurunui District Council, acting under the Local Government Official Information and Meetings Act 1987 (LGOIMA) and specifically the Standing Orders and meeting conventions of the Hurunui District Council.
Status of Workshops Workshops are a common tool used by councils and are a legitimate part of the governance process. Generally, a Council or a committee may hold a workshop in the early stages of drafting a position or direction on a policy or planning matter. The result is that officers then feed that discussion and information into a report that would eventually make its way back for open discussion, debate and decision making in a formal meeting. Some councils also hold briefings, which is more of a one‐way information sharing process for officers to inform members of matters that may not yet be public, which may be confidential for a variety of reasons or to convey detailed information to enable the decision makers to be better prepared when considering complex matters. Another common approach is the use of smaller working groups, which are in the same way an informal meeting, but for a specific purpose or project. The Hurunui District Council for example, currently has eight working groups that meet as required and are working on a number of different issues. The Council
18
provides a basic summary of progress on each of these at every Council meeting. Eventually the work of these sub‐groups will feed into a public decision making process.
Workshops, briefings and working groups do not fall under the requirements of LGOIMA or Council Standing Orders, as they are not formal meetings and no decisions are allowed to be made at these meetings. It is generally accepted practice that workshops are not a substitute for open debate on issues that are matters of public interest. As these are not formal meetings, it is the prerogative of the Committee to decide whether or not to make them open to the public and indeed whether there is any public notification of them. At the Hurunui District Council, individual members are encouraged to always scrutinise and challenge if necessary, any decisions to hold public excluded meetings and by extension, members‐only workshops.
The key point to note is that there is no obligation for workshops or briefings to be open to the
public as they have no formal status as a meeting. Therefore there are no set rules about how they
operate, but a Council or Committee is obliged to still ensure that good process is followed and to
be mindful of the purpose of local government which is clearly stated in the Local Government Act
as being, among other things, to enable democratic local decision‐making and action by, and on
behalf of, communities. It is important that the Committee does not substitute workshops for
meetings where the matter can realistically be discussed in an open meeting. Where there is a
members‐only workshop notified on a public meeting agenda, a good approach is for the
Committee to provide an explanation of the subject, who is attending, the reasons for it being
members‐only and at a later stage, some form of report back or summary of the discussion, subject
to any confidential information being withheld. As there are no decisions made in workshops or
briefings, there is no requirement for minutes or notes to be taken and generally there are no
meeting secretaries in attendance, so any report back would be a summary by an officer or perhaps
the Chairperson or a Committee member.
Public Perception As with many situations, it is not only the rules that committee members need to be mindful of but the matter of public perception. If there is a members‐only workshop prior to a meeting and it is discussing the same matter that is on the meeting agenda, then it can appear to the public that what should be a public discussion is happening behind closed doors and the Committee meeting itself then just becomes a rubber stamp process, which can be seen to undermine the integrity of the democratic decision‐making process and the purpose of local government.
Public Excluded Rules and Procedures It may be useful to reiterate that the Zone Committee can resolve to hold public excluded discussions as part of its formal agenda business and to do so it must apply one or more of the clearly defined reasons in LGOIMA. The more common reasons used for the Zone Committee would be to protect the privacy of individuals being discussed or for reasons of commercial sensitivity. It is important to note that “free and frank discussion” is not an applicable reason for holding a public excluded meeting. It is acknowledged that the terminology used for recent workshops as being “public excluded” may not be the best approach as this infers that the Committee is relying on the formal public excluded reasons for excluding the public from a meeting. A better way to refer to these workshops are as members‐only workshops or briefings. There is also no obligation on the Committee to publicly notify these workshops, but the current practice of including it on the meeting agenda coversheet is for the benefit of members to ensure they are fully notified of the schedule for that day. This creates a situation of effectively publicly notifying the workshop and triggers the need to at least inform the public about the subject and reasons for it.
19
Zone Committee Operating Philosophy The Zone Committee has a commitment to openness, transparency and collaboration that is reinforced through its Terms of Reference and the Code of Conduct for members. The Zone Committee has in the past held many workshops that it has made open to the public and only holds members‐only workshops where good reasons exist, like for example to speed up the delivery of solutions to complex problems, to allow members to be exposed to a variety of perspectives that may not be forthcoming in a public meeting and to identify and resolve potential conflicts that may be hindering progress being made on key outcomes. The Zone Committee has a very inclusive approach to its meetings and allows participation from the public gallery, which is a privilege that is not allowed for in normal Committee and Council meetings, where public participation is strictly controlled by Standing Orders. It is clear that there is no intention from the Zone Committee to be closed and deliberately seeking to exclude public involvement in its processes.
Recommended Approach It is accepted that holding workshops, some of which may be members‐only, is a normal way of operating and of working through complex and sometimes sensitive issues. It is recommended that in future the terminology used will be as “members‐only” rather than “public excluded” workshops. It is acknowledged that finding time when all members are available is difficult, so holding workshops adjacent to formal meetings is sensible for reasons of expediency. In general the Committee should avoid holding a members‐only workshop prior to a meeting where there is an agenda item on the same matter. Where this is considered unavoidable due to timing or scheduling constraints, it is recommended that at the beginning of the public meeting the Chairperson or Zone Committee Facilitator provide a brief oral summary of the workshop, ensuring that any confidential matters are not discussed. This would assist in the Committee being as open and transparent as possible. If the matter is not being discussed at the meeting immediately following, then a summary of the workshop can be provided in two ways, as part of a formal report on that matter to a subsequent meeting, or as a specific update item, with a brief summary provided, but once again, ensuring that no confidential information is shared. When a members‐only workshop is effectively publicly notified on an agenda coversheet, the subject matter, the reasons for it being members‐only and who is attending should be explained.
20
AGENDA ITEM NO: 7
SUBJECT MATTER:
Mata Kopae / St Annes Lagoon
REPORT TO:
Hurunui‐Waiau Zone Committee
DATE OF MEETING:
11 December 2017
PREPARED BY:
Leanne Lye (Acting Zone Manager)
ACTION:
For decision
Purpose The Hurunui Waiau Zone Committee have committed to implementing 2 mahinga kai projects in the district through its 5 year objectives. This is an opportunity to determine if the committee are interested in pursuing a Mahinga Kai project at Mata Kopae/ St Annes lagoon and the best option to enhance this work. Cultural Values Mahinga kai properly refers to Ngāi Tahu interests in traditional food and other natural resources and the places where those resources are obtained. Mata Kopae is rich in tuna (eel) and waterfowl. It is home to a range of indigenous wetland species and shrubs. It is an important site for Te Rūnanga o Kaikoura. Background Due to the impact of the drought in Hurunui over 3 years, Mata Kopae commonly known as St Annes lagoon dried out earlier this year. St Annes lagoon is situated north of Cheviot and is the responsibility of Hurunui District Council. The drought had a detrimental impact on the eel habitat and in February a group of concerned locals and staff from Environment Canterbury, Department of Conservation and other organisations organised an eel rescue. A concerned Hurunui District Councillor approached the Zone Team asking what could be done and the suggestion that digging a hole in the lagoon would keep enough water in the lagoon to prevent the eel habitat being compromised. With the impact of global warming there is a high chance of increased droughts on the east coast and this will have a negative impact on the eel habitat. Environment Canterbury has used its science team to look at 2 mitigation options. The first option was to deepen the lagoon by digging a hole. Core sampling was undertaken at different sites to get a better understanding of the soil type. The report concluded that removing the sediment layer would not have any long‐term benefit to the eel habitat (report attached). The next option was to look at augmenting water into the lagoon. A high‐level report (attached) shows that this is a feasible option but would require the cooperation of several different parties.
21
To date a meeting has been held with Robb MacBeth & James Paterson, they have given their support if we wanted to look at water augmentation and are keen to work on this collaboratively. A meeting is scheduled with Cr Vince Dally on Friday 8th December to investigate the work he has completed on his lagoon. An initial discussion with Te Rūnanga o Ngāi Tahu (TRONT) has been held, this was positive and a meeting will be held within the next week to discuss further. Options Option 1 – status quo Do nothing and let nature run its course. When the lagoon runs dry there may be a need for the local community to band together and rescue eels when required. Does not unnaturally disturb the lagoon. No costs associated with this. Option 2 – deepen the lagoon Dig a hole in the lagoon which will hopefully hold and ensure enough moisture is retained in the lagoon in a drought. This would disturb the bed of the lagoon. A resource consent from Environment Canterbury for work in a waterway would be required. Evidence suggests there is no long term benefit to doing this. No guarantee how long this would work for. Costs for consent approx. $2,000 Costs for sediment removal $1‐$2,000 approx Option 3 – water augmentation Augment water from the Waiau river utilising the existing piping infrastructure of Phoebe irrigation. This would make it a collaborative project with Hurunui District Council, Environment Canterbury, the local community, Phoebe Irrigation. This would require resource consents from Environment Canterbury for water abstraction and water discharge. This is the costlier option of the 3 but has the best long‐term benefits. Robb MacBeth from Phoebe Irrigation and James Paterson, adjoining land occupier have already signaled their willingness to work with the Zone Committee on this option. Long term it provides a level of comfort knowing that there is the opportunity to augment water ito the lagoon prior to the irrigation season in readiness of a dry summer. Costs for consents approx. $5,000 Cost for installing Water level reader $6,000 (there maybe other cheaper options we could look at) ongoing costs of maintenance ($6,000) Costs for pumping water approx. $0.06 ‐ $0.10 / m3 Recommendation Without having the opportunity to consult with all parties due to the close turnaround time between Committee meetings but based on the initial information supplied that the zone committee decide on an option that they feel has the best outcomes for Mahinga kai outcomes at Mata Kopae.
22
St Annes lagoon – March 2017
St Annes lagoon – June 2017
23
Memo
Mata Kopae/St Anne’s Lagoon is a small, shallow lake and associated wetland, located just north of Cheviot in North Canterbury. The ‘lagoon’ is approximately 0.15km2 and the contributing catchment area is about 2.3km2. It is located in the headwaters of a tributary of Caroline Stream, which feeds into the lower Waiau River. The surrounding landscape is eroded pastoral hill country with an average annual precipitation of approximately 700mm. The small lake is solely reliant on rainfall runoff to maintain its water level.
Mata Kopae/St Anne’s Lagoon has high amenity/cultural values, is rich in tuna and waterfowl and home to a range of indigenous wetland species and shrubs. It is a significant site to Te Rūnanga o Kaikōura, with strong mahinga kai associations. In recent years projects have been undertaken to restore the lake and wetland.
In February 2017 after three years of lower than average precipitation Mata Kopae/St Anne’s Lagoon dried up for the first time in nearly 50 years. According to anecdotal evidence the last time the lake dried up was in the early 1970’s. Concerns were raised about the drying of the lagoon and we were asked to investigate what could be done to avoid this from happening again and to consider possible mitigation measures.
Two mitigation options were suggested:
- Deepening of the lagoon
- Flow augmentation into the lagoon
Deepening of the lagoon:
Work undertaken in April 2017 by Hamish Graham (ECan Hydrogeologist) indicates deepening the lagoon is not feasible. This work was presented at one of the Zone Committee meetings earlier this year.
Augmentation flow into the lagoon:
As a first stage, a high-level feasibility assessment has been carried out. A basic water balance model, using storage, precipitation and evaporation data, was set up to work out flow augmentation requirements to maintain water levels within a range to sustain the ecological health of the lagoon. The main assumptions and input data used are:
- Precipitation and Evapotranspiration data (VCSN and data from a weather station at
Cheviot) from January 1971 to July 2017;
- Profile Available Water (PAW) and loss rate based on soil data (Landcare Research
s-map database);
Date 17 November 2017
To Leanne Lye
From Jeanine Topélen
24
- Lagoon area and storage volume at different lake levels (lagoon survey carried out by
Envirolink), maximum storage is 180,000m3;
- Critical storage level is 72,000 m3 (0.4 * maximum storage level to maintain life
supporting capacity for tuna);
- Trigger storage level to start flow augmentation into the lagoon is 135,000m3;
- Robb MacBeth (Phoebe Irrigation Ltd) is willing to allow the flow augmentation to be
supplied via the existing infrastructure of Phoebe Irrigation Ltd. To ensure that the
reliability of supply for Phoebe Irrigation Ltd is not affected flow augmentation of the
lagoon will only occur if the critical storage level is breached in the month
September. No flow augmentation will occur in other months of the year. Water
available for augmentation will only be unused consented Phoebe Irrigation LTD
water and we have assumed we will be allowed to continuously discharge into the
lagoon at maximum rate. The cost to use the existing infrastructure will be $0.10 per
m3 (pers. comm. Robb MacBeth);
- The cost to install and maintain a water level recorder, for monitoring and
management purposes, in the lagoon will be approximately $6,000 for the
installation and $6,000 for ongoing maintenance (pers. comm. Phil Downes, ECan).
The results of modelling the lagoon storage are shown in the figure below. The figure shows two hydrographs; lagoon storage over time without augmentation (blue) and lagoon storage over time with augmentation when required (grey). The critical storage level is shown as the orange line.
The critical storage level would have been breached in five years over the modelling period, so flow augmentation would have been required five times. The indicative costs associated with this flow augmentation based on $0.10 per m3 is shown in the table on the next page.
25
It is noted that the above assessment is only a high-level assessment to provide an indication of feasibility and cost of flow augmentation into the lagoon. Should any of the assumptions change, flow augmentation requirements and associated costs are likely to change as well.
water year Indicative flow augmentation costs ($)
1971 0
1972 0
1973 0
1974 0
1975 0
1976 0
1977 0
1978 0
1979 0
1980 0
1981 0
1982 0
1983 0
1984 0
1985 0
1986 0
1987 0
1988 0
1989 0
1990 0
1991 0
1992 0
1993 0
1994 0
1995 0
1996 0
1997 0
1998 5624.64
1999 0
2000 0
2001 0
2002 0
2003 0
2004 0
2005 0
2006 0
2007 2410.56
2008 0
2009 0
2010 0
2011 803.52
2012 0
2013 0
2014 0
2015 4821.12
2016 4821.12
26
Memo
Subject: Mata Kopae/St Annes Lagoon subsurface investigation
1 Background
In February 2017 Mata Kopae/St Annes Lagoon ran dry. The lagoon has an abundance of eels living in the waters/mud. An eel rescue effort was subsequently undertaken during which over 2000 eels were rescued from the muddy lagoon bottom.
At this time it was suggested by a Hurunui District councillor that a hole be dug in the lagoon to provide refuge for aquatic life for next time the lagoon goes dry. One of the biggest potential concerns with undertaking this is that digging a hole could in fact drain the lagoon faster by opening a conduit to any freely draining gravels underlying the muddy lagoon bottom. As such, the Groundwater Science team undertook an investigation of the subsurface geology below the lagoon to better understand what is there and whether the proposal will drain the lagoon quicker.
2 Methodology
To understand the subsurface geology a series of exploratory holes (up to 4 m below the lagoon bottom) were hand augured into the bed of the lagoon. The primary focus of this was around an island at the southern end of the lagoon. The location of the island and hand augur holes can be seen in Figure 1.
Figure 1: Location map of hand augur locations
Date 6 April 2017
To Leanne Lye
cc
From Hamish Graham, Hydrogeologist
27
3 Results/Discussion
The bore logs from the hand auguring can be seen in Appendix 1. BH1, BH2 and BH5 were drilled around the island at the southern end of the lagoon. This is the proposed location of the hole. The auguring found a top layer of lagoon deposit (brown silty sand with some organic material) with a thickness of up to 1.25 m. This unit is the “mud” that the eels had burrowed into and were subsequently rescued from. At the time of drilling this unit was unsaturated and the only water in the vicinity was a small amount of ponding from recent rainfall. There was minimal water in the lagoon deposit with the water that was present related to recent rainfall. Below this layer to the termination depth of 4 m (this was as far as we could augur with the equipment) there was a hard clay unit with containing varying amounts of silt. This unit was unsaturated and hard to augur through.
If a hole were to be dug in the close vicinity of the island (a trench around the lagoon for example), then as long as it was less than 4 m deep then there should not be a risk of draining the lagoon quicker. However, during auguring there was no apparent groundwater in either the top lagoon deposit layer or the clay/silt layers. Therefore, any water that does pond in the hole is likely to evaporate relatively quickly. It is unlikely that the eels will be able to burrow into the hard clay.
BH3 (western lagoon extent) and BH4 (northern lagoon extent) were drilled to help understand the subsurface geology across the lagoon. These two holes encountered different geology to that encountered around the island, with more sand present in BH4 and more water in BH3. This variability means that the greater than 4 m to gravel conclusion should only be considered in the near vicinity of the island.
28
Appendix 1: Bore logs
BU26/0017 (BH1)
29
BU26/0018 (BH2)
30
BU26/0019 (BH3)
31
BU26/0020 (BH4)
32
BU26/0021 (BH5)
33
1
HHurunui District Landcare Group Memorandum
3rd December 2017 To Ned Norton – Environment Canterbury From Joshua Brown – Hurunui District Landcare Group Subject: Interim results from research into potential impact of permitting dryland farming Status: DRAFT
1. Key findings Key conclusions from the survey of 66 predominately dryland farms were:
Surveyed farms showed an increase of 7.4% in wintered Relative Stock Units (RSUs) over the last 10 years (2007 to 2017).
This equates to an average historic rate of change of +0.74% per year in RSUs Surveyed farmers intended over the next 10 years to increase RSUs by +10% (+1%/yr).
Key conclusions from the 10 case study dryland farms were:
Current rootzone losses from dryland farms range from 8 kgN/ha/yr to 26 kgN/ha/yr. The average loss was 12kg-N/ha/y for the total farm area. Excluding ineffective areas (e.g. native
bush) the average loss was 16 kg-N/ha/y. The historical change in nitrogen rootzone loss for all 10 farms, was an increase of +0.17%/yr At a farm scale this ranged from -10% over a 16 year period(-0.63%/yr) to +56% over a 14 year
period (+4%/yr)
The summary conclusion is that the rate of change of dryland farming systems (over long periods) is much slower compared with the rate of change that can occur with the introduction of irrigation. While stock numbers can fluctuate from year to year in response to climate variability, over the longer term the carrying capacity and land use options are fundamentally limited by the unpredictable, erratic dry climate. Dryland farming has occurred in the Hurunui and Waiau catchments for the last 160 years. Over this period changes have generally been slow and incremental. Over the next 6 years (until 2023 when the HWRRP is reviewed) it seems quite unlikely that there would suddenly be a large step-change in the rate of change. The low rate of change on a catchment scale infers dryland farming will likely have a very minor impact on Hurunui and Waiau mainstems nitrogen loads for the foreseeable future.
1. Scope Environment Canterbury asked the Hurunui District Landcare Group (HDLG) to assess the potential nutrient impact if dryland farming were made a permitted activity in the Hurunui and Waiau catchments. The two key questions were:
What is plausible dryland farm development? What is the likely impact of permitting dryland farming?
HDLG undertook two main pieces of work to answer these questions - a survey of 83 dryland farms, and a more detailed nutrient assessment for 10 of these farms. The general survey provides insight into what plausible development is likely at a catchment scale. The case study assessments were used to estimate what this plausible development would likely mean for nutrient losses reaching the
34
2
Hurunui and Waiau River mainstems. This memorandum focuses on rates of change and the case study results. Further results from the analysis of the research is to come as outlined in section 6.
2. Background Hurunui District Landcare Group The HDLG is an incorporated society with a committee of 15 farmers and a current membership of 120 predominantly dryland farmers. The members cover 111,000 hectares in the Hurunui / Waiau zone which represents approximately 20% of the farmed land.
Item 1. Aerial photos of the Hurunui and Waiau Catchments
35
3
3. Methodology Survey The HDLG undertook a survey (Appendix 1.) of its members to get an understanding of their members farming practices, where they had come from and where they are heading. The analysis in this memorandum focuses on the questions regarding historic, current and predicted stock numbers. I have included a short section on winterfeed, however this section has yet to be fully analysed with supporting industry data.
In total 83 farms were surveyed. 6 responses were excluded due to outlying results and another 11 were excluded due to having a large (>50ha) area of irrigation. This left 66 farms for analysis. These farms covered an area of 70,000ha in the Hurunui and Waiau catchments with a total of 61,000 effective hectares. This represents 24% of the total area in the Hurunui and Waiau catchments below the Mandamus and Marble Point.
Farmers were asked their wintered stock numbers by stock class for 10 years ago, current where they think they will be in 10 years’ time. Stock numbers were converted to RSUs and summed. This conversion is in table 2 below. These numbers were then aggregated to give an overall picture of change in stock units.
conversion factor Sheep Cattle Deer
1.1 5 1.9 Table 1. Stock number to Relative Stock Unit (RSU) conversion factor1
Case studies 10 HDLG farms had historical changes modelled in OVERSEER to quantify the impact of dryland farm development on nitrogen loss. Each farm had a nutrient budget generated for a time in the past and current day. The information for the historical nutrient budgets varied from being 6 – 45 years ago with the average period being 24 years ago. I compared stocking rates and rate of change from the case study farms and found them similar to the wider survey.
The case study farms were also spatially modelled in a GIS program for a comparison between OVERSEER root zone losses, the in-river nitrogen load layer (P.Brown, 2017) and Environment Canterbury’s nitrogen rootzone loss layer. This work and the methodology for this is presented in the comparisons section.
1 The same conversions are used in Beef + Lamb NZs economic service data
36
4
4. Results Rate of change While there was variation on individual farm RSUs changes from -19% to +75%, the overall trend showed that on a catchment scale, changes happen at an incremental pace. Variation on individual farms also show remnants of the drought, with many responses showing present RSUs being down but past and future RSUs to be constant.
Past (2007)
Present (2017)
Current farmer
intentions (2027)
Relative Stock Units (RSU)
336234 363275
399720
% change +7.4% +10.0% Table 2. Shows summary of change in change in stock units from survey results
There has been a slight shift in stock type ratios with a downward trend in sheep and upward trend in cattle and deer. This trend is also predicted to continue. This put in conjunction with the slow rate of change however still shows the incremental shifts that happen on dryland farms.
Wintered Stock
Past (2007)
Present (2017)
Current farmer
intentions (2027)
Sheep 71.9% 70.1% 66.5%Cattle 26.3% 28.0% 31.2% Deer 1.8% 1.9% 2.3%
Table 3. Shifts in stock type ratios
Putting these shifts in comparison in changes in the market, such as dairy pay out, beef price and lamb price, it shows that even when opportunities are present in any given year, on a catchment scale, the change is still very gradual.
These results show that the rate of change in RSUs has only been about 0.9% per annum and is likely to be similar over the next 10 years.
Note:
Beef + Lamb NZ Economic Service data shows a long term decline in RSUs in the Hurunui. The reasons for this trend difference have not yet been fully explored. This does however indicate that results and trends from the HDLG survey are likely to be overestimating an increase in RSUs rather than underestimating. The reasons and impact of the differences here will be explored in reports to come.
37
5
Nitrogen root zone loss increases The nutrient budgets showed:
An overall increase of 4.1% in nitrogen root zone loss with a 14.7% increase in RSU’s across the 10 farms.
Nitrogen root zone loss varied from 8kgN/ha/yr to 26kgN/ha/yr the current day nutrient budgets. The weighted average by farm area nitrogen loss was 12kgN/ha/yr
Variation in % change in nitrogen loss was -10% over a 16 year period (-0.6%/yr) to +56% over a 14 year period (+4.0%/yr).
Variation in % change in stock units was -22% over 40year period (-0.6%/yr) to +47% over 14year period (+3.6%/yr).
Topography Rainfall kgN/ha/yr Total
RSU
% change
RSU
%change nLoss
Change Period (years)
Farm1 current Flat 769 18 3411 4.99% -10% 16 Farm1 historic Flat 769 20 3249 Farm2 current Flat 716 17 6635 -9.12% 0% 27 Farm2 historic Flat 716 17 4323 Farm3 current Easy Hill 993 15 8151 -6.90% -6% 20 Farm3 historic Easy Hill 993 16 8755 Farm4 current Easy Hill 801 22 3407 11.74% 5% 6 Farm4 historic Easy Hill 801 21 3049 Farm5 current Easy Hill 628 14 11019 47.49% 56% 14 Farm5 historic Easy Hill 628 9 7471 Farm6 current Rolling 597 15 5078 38.33% 7% 20 Farm6 historic Rolling 597 14 3671 Farm7 current Rolling 815 12 5875 15.15% 20% 20 Farm7 historic Rolling 815 10 5102 Farm8 current Steep Hill 1328 8 5247 -22.39% -11% 40 Farm8 historic Steep Hill 1328 9 6761 Farm9 current Easy Hill 954 26 8375 1.11% 24% 30 Farm9 historic Easy Hill 954 21 8283 Farm10 current Easy Hill 765 12 3876 49.54 20% 45 Farm10 historic Easy Hill 765 10 2592
Table 4. Case Study OVERSEER modelled results
Farm 8 covered 1/3rd of the total case study area. Separate analysis of the results, excluding farm 8 showed:
An overall increase of 19.6% in nitrogen root zone loss and a 20.1% increase in RSUs. A weighted average by farm area in nitrogen loss of 16.2kgN/ha/yr
The case studies outline the likely range of nutrient losses and the rate of change in nutrient loss. This, plus the survey results shows that while there is variation on individual farm scale, the overall impact from dryland farming change is likely to be very low.
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6
A summary of the types of development options employed by these farms and the associated nutrient change is a work in progress.
Winter Crop Farmers were asked in the survey for winter crop area for cattle, sheep and deer. The interim results from this work showed:
An average winterfeed area of 2.7% of the total farm area with a maximum area of 12.5% and a minimum of 0%.
1.1% average winter crop area for cattle grazing 1.6% average winter crop for sheep grazing Excluding those that had no winterfeed there was an average area of 16ha for cattle and 24.5ha
for sheep Note that there is likely a cross over between areas grazed by sheep and areas grazed by cattle
Further analysis of dryland winter crop area in the Hurunui and Waiau is being done and will be presented in the new year.
39
7
5. Comparisons In the Hurunui and Waiau there have been two other methods, other than OVERSEER, used to estimate the nutrient losses from dryland farming. These methods have been outlined below and compared with the OVERSEER estimates from the 10 case study farms.
Ground truthing ECan nitrogen loss layer for dryland farms Environment Canterbury presented a draft GIS nitrogen loss ‘lookup table” earlier in 2017. This method spatially represented previous modelling done through the MGM project.
Item 2. ECan Draft GIS nitrogen loss estimate layer
It relies on information that is publicly available such as satellite imagery, Land Cover Database and AgriBase survey data. The HDLG was asked to ground truth the dryland component of land-use layer and associated nitrogen loss layer. while AIC would provide verification for the irrigated areas.
While difficult to do on an individual farm scale the land-use layer on a catchment scale seems relatively consistent with farm land-use. I did compare case study farms for a detailed comparison and found these to be roughly similar to actual land use. More work is to be done on this to compare this layer at a finer scale.
40
8
HDLG was also able to draw on the OVERSEER budgets done as a part of the dryland research and compare these with ECans MGM Nloss layer. The summary is provided in table 5 & 6.
In-river (kgN/ha ECan
mgm Nloss
OVERSEER kgN/ha/yr
ECan vs Overseer
difference
Farm1 Flat 18.5 18 -2.6% Farm2 Flat 18.3 17 -7.6% Farm3 Easy hill 10.2 15 31.7% Farm4 Easy hill 10.5 22 52.3% Farm5 Easy hill 2.7 14 80.7% Farm6 Rolling 10.8 15 28.2% Farm7 Rolling 16.0 12 -33.1% Farm8 Steep hill 3.2 8 59.7% Farm9 Easy hill 16.8 26 35.4%
Farm10 Easy hill 7.1 12 40.8% Average 6.6 12.0 -45%
Table 5. ECan MGM compared to OVERSEER on dryland farms
The key conclusions from this are:
On flatter topography there is a correlation between ECan mgm nitrogen rootzone loss estimates and OVERSEER nitrogen root zone loss estimates.
On extensive hill country there was a significant difference between ECan Mgm rootzone losses and OVERSEER rootzone losses.
Further work is needed to fully explore this difference in rootzone loss estimates on extensive hill country.
Extensive hill country component
Nloss
ECan MGM loss (kgN/ha/yr)
OVERSEER (kgN/ha/yr)
Factor difference
Farm3 0.5 10 20.0 Farm4 6.5 23 3.5 Farm5 2 10 5.0 Farm7 1 12 12.0 Farm8 0.5 11 22.0 Farm9 0.5 7 14.0
Table 6. Comparison of extensive hill country areas on the case study farms showing the difference between the ECan mgm nitrogen loss estimates for that area and OVERSEER estimates
41
9
In-river nitrogen load layer I compared the case study OVERSEER results with the in-river nitrogen load calculators prepared by Peter Brown (Brown, 2017, 2015, 2014). Peter Brown used water quality samples from numerous sites in the Hurunui and Waiau to estimate contributions of nitrogen from differing land classes. These land classes were then spatially mapped. This method was presented several times to the Hurunui/Waiau science stakeholders group and nutrient working group.
Item 3. Brown (2017) in-river load layer
To compare the OVERSEER results, I clipped the in-river load layer to the spatially mapped case study farms. Then using the nitrogen loss table below (Brown, 2017) I summed the in-river attributed load.
Class Load Description 1 29.0 Irrigation 2 3.5 Dryland<15° (tractor country) 3 1.4 Dryland>15° (high country) 4 0.3 Exotic forest & scrub 5 0.3 Non-agricultural (e.g. Native forest, alpine)
Table 7. (Brown, 2017) in-river nitrogen load attribution to land-use
To allow for the variation in total area (due to farm boundary differences), I converted both results to kgN/ha to allow for a direct comparison.
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10
The results from this comparison are displayed in the tables below:
InRiver
ECan Mgm nloss
OVERSEER
Area (ha) 13020 13076 13570 Total kgN 18525 85562 162634 kgN/ha 1.4 6.5 12.0
Comparison Factor 4.6 8.3 Estimated % of below root zone Nloss likely to reach
maintstem of river from this method
22% 12%
Table 8. Comparison between aggregated OVERSEER estimated below rootzone nitrogen loss from case study farms and the in-river nitrogen attribution from P.Browns in-river load layer.
Notes:
For this process, case study farm 10 was excluded as the in-river load layer did not cover its area. The small variation in in-river area verses ECan nloss area is due to a 56ha block off one of the
case study farms that was outside the catchment and not covered by the in-river layer. The OVERSEER area difference is due to farm ownership boundaries varying from actual farmed area. These variations make negligible difference to the overall difference in the comparison.
As discussed earlier, farm 8 was a large portion of the total case study areas. As such I have also calculated the comparison excluding farm 8 & farm 10:
InRiver
ECan Mgm nloss
OVERSEER
Area (ha) 6163 6219 6622 Total kgN 15806 63437 110057.0 kgN/ha 2.6 10.2 16.6
Comparison Factor 4.0 6.5 Estimated % of below root zone Nloss likely to reach
maintstem of river from this method
25% 15.4%
Table 9. Comparison calculation excluding farm 8 & 10
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11
6. In-progress There are several pieces of work from the dryland farm research that are currently progressing towards presentation for the HWZC in the new year. These include:
An analysis of winterfeed trends in the Hurunui and Waiau catchments and the parameters that constrain future dry land development.
A summary of the types of development options available to dryland farmers and their impact on nutrient loss.
An analysis of the Good Management Practice question results from the survey and the potential the results imply for associated nutrient loss reductions
7. References Brown, P. (2014). “Statement of evidence of P Brown for Ngai Tahu Properties consent application
CRC144606”, 20 May 2014
Brown, P. (2015). “Hurunui River nutrient modelling: impact of dryland intensification”. Memorandum dated 15 March 2015. Prepared for the Hurunui, Waiau and Jed Nutrient Working Group.
Brown, P. (2017). “Hurunui and Waiau catchment nutrient calculators”. Memorandum dated 6 November 2017. Prepared for Ned Norton
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12
Appendix Dryland Farm Survey
Question Answer Rating HDLG Number
Farm Name
Farmer
Contact Number
Farm Block Address 1
Farm Block Address 2
Farm Block Address 3
Farm Block Address 4
Total Farm Area Effective Farm Area Irrigated Area Winter Crop for Cattle Area Winter Crop for Sheep Area Winter Crop for Deer Area Summer Crop Area
Farm Environment Plan completed for the Farm. (How often do you look at it)
Nutrient Budget completed for the farm
Effective land area 10 years ago Current wintered sheep numbers Wintered sheep numbers 10 years ago 10 year prediction of sheep numbers Current wintered Cattle numbers Wintered Cattle numbers 10 years ago 10 year prediction of Cattle numbers Current wintered Deer Numbers Wintered Deer numbers 10 years ago 10 year prediction of wintering Deer Do you have soil moisture measuring tools (ie soil moisture tapes, probes) that you use to decide when to turn on the irrigators
Rainfall records are kept and rainfall forecasts monitored and used in decision making
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13
Full pre-season maintenance checks undertaken on irrigators
Bucket test done on all irrigators within the last 3 years
Bucket tests showed adjustments needed to be made
Adjustments were made to fix the issue found in bucket tests
Staff have been trained in irrigation procedures
Do you use conventional fertiliser
Are you aware of the spreadmark certification program for fertiliser spreader operators
Are spreadmark certified spreaders available in your area
Contractors used for fertiliser spreading are spreadmark certified
Do you spread your own fertiliser
Is your own fertiliser spreading equipment calibrated according to manufacturer’s recommendations
Intensive land area that receives nitrogen fertiliser annually
Average annual application rate of nitrogen on intensive land
Extensive/hill area that receives nitrogen fertiliser annually
Average annual application rate of nitrogen on extensive/hill country
Intensive land area that receives Phosphorus fertiliser annually
Average annual application rate of phosphorus on intensive land
Extensive/hill country area that receives phosphorus fertiliser annually
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14
Average annual application rate of phosphorus on extensive/hill country
Fertiliser is not applied when the soil temperate is less than 10 degrees
GPS technology is used for precise application of all fertiliser spread (e.g. Proof of placement)
Stock are excluded from permanently flowing waterways in intensively grazed areas
Cattle and deer are excluded from waterways on paddocks with average slope less than 15 degrees
Over what proportion of your extensive/hill country do you rely on surface water for stock drinking
What is your preferred method of cultivation (direct drilled, minimum tilled, conventional tillage)
Do you leave gullies and swales uncultivated on rolling down country (refer photo)
Uncultivated buffer strips of at least 2m on flat land and wider on sloping land are left to filter any runoff
Deer are provided with out of creek wallows
Effective measures are taken to prevent fence line pacing (very little fence line pacing)
How many sediment traps/dams do you have? (Mark on map)
Riparian plantings are established in gullies
Riparian planting programme prepared
Do you actively protect vegetation biodiversity and wetlands
how many km of fencing for above
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15
Area of Pest Trapping for above
Area of weed control for above
How many km of permanently flowing waterways do you have
Do you actively protect permanently flowing waterways
How many km of fencing for above
Can you describe the change in biodiversity on your property over the last generation (area and predator control)
Additional Comments (Anything that you do that you believe protects or enhances the environment)
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AGENDA ITEM NO: 10 SUBJECT MATTER:
Establishing a subcommittee to progress discussions with AIC on further deferring a consent review in relation to HWRRP minimum flows
AUTHOR: Ian Whitehouse, Environment Canterbury
DATE OF MEETING: 11 December 2017
Action required
1. Establish a subcommittee to progress discussions with AIC on further deferring a consent
review in relation to HWRRP minimum flows;
2. Agree the Terms of Reference for the subcommittee;
3. Appoint zone committee members to the subcommittee.
Background
As part of addressing the key water issues for the zone the committee will be making
recommendations at the end of March 2018 to Environment Canterbury on the timing of a review of
consents in relation to the HWRRP minimum flows.
The committee is considering whether further deferring a consent review could lever more action to
improve water quality and biodiversity.
AIC has told the committee that implementing the HWRRP minimum flows would impose significant
cost to the irrigation company and its shareholders to construct water storage and through dairy
farmers having to purchase additional feed.
AIC has shared with the committee their thoughts on projects that could improve biodiversity or
water quality.
The committee is at the stage where it wishes to have further discussions with AIC on what could be
achieved if a consent review was further deferred (noting that the committee wants the minimum
flows to be implemented sooner rather than later).
The committee believes these discussions are best led by a small subcommittee working closely with
the full committee.
A draft Terms of Reference for the subcommittee is attached.
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HWZC Consent Review Subcommittee
Draft Terms of Reference (04 December)
Purpose
The subcommittee will lead the Hurunui Waiau Zone Committee’s discussion with Amuri Irrigation
Company (AIC) on the timing of a review of water take consents to fully implement the Hurunui
Waiau Rivers Regional Plan (HWRRP) minimum flows.
Background
The HWRRP became operative in December 2013 and introduced new minimum flows.
The Zone Committee wants the HWRRP minimum flows to be implemented sooner rather than later.
The HWRRP minimum flows only apply for existing water takes when consents are renewed unless
there is a consent review.
AIC is one of the largest water‐take consent holders for both Hurunui and Waiau Rivers. Their water
take consents are to 2033.
Following the HWRRP becoming operative AIC and their shareholders told the Zone Committee that
a consent review would divert resources from activities to improve nutrient management.
In an exchange of letters with Environment Canterbury the Zone Committee recommended that a
consent review be deferred until at least the end of 2017 with the expectation AIC would complete
specified activities relating to audited farm environmental plans. These activities have largely been
completed.
As part of addressing the key water issues for the zone the committee will be making
recommendations at the end of March 2018 to Environment Canterbury on the timing of a review of
consents in relation to the HWRRP minimum flows.
The committee is considering whether further deferring a consent review could lever more action to
improve water quality and biodiversity.
AIC has told the committee that implementing the HWRRP minimum flows would impose significant
cost to the irrigation company and its shareholders to construct water storage and through dairy
farmers having to purchase additional feed.
AIC has shared with the committee their thoughts on projects that could improve biodiversity or
water quality.
The committee is at the stage where it wishes to have further discussions with AIC on what could be
achieved if a consent review was further deferred (noting that the committee wants the minimum
flows to be implemented sooner rather than later).
The committee believes these discussions are best led by a small subcommittee working closely with
the full committee.
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Subcommittee membership
The subcommittee will comprise those committee members appointed by the zone committee.
Subcommittee scope
The subcommittee will lead discussions with AIC on behalf of the zone committee.
The subcommittee cannot make decisions on behalf of the committee. Recommendations or
decisions arising from the discussions with AIC require consensus agreement from the zone
committee.
The focus of the discussions with AIC will be:
The timing of a consent review (noting that the committee wants the minimum flows to be
implemented sooner rather than later);
The actions that AIC would achieve if a consent review was deferred for a specified period
(say 2 years, five years).
The discussions will not include a requirement of a plan change to make major water storage easier.
While the committee is open to such a plan change and for it to be included in changes to the
HWRRP to be notified in 2018, the committee considers AIC needs to provide such a plan change,
with the technical evidence necessary to ensure it is widely supported.
The subcommittee will work with the Zone Committee to develop guidance for the discussions with
AIC including bottom lines and desired outcomes. This guidance will be revised and updated with the
zone committee as required and could include dollar values to mitigations that will be considered.
Timetable
The committee will make recommendations on the timing of a consent review to Environment
Canterbury at the end of March 2018. The subcommittee will endeavour to reach agreement with
AIC by mid‐March on the timing of a consent review and the actions that AIC will undertake.
The zone committee expects to still make a recommendation to Environment Canterbury on a
consent review even if no agreement has been reached with AIC. This recommendation is likely to be
to review consents in 2021/22.
Subcommittee reporting to Zone Committee
The subcommittee will keep zone committee members fully informed of the discussions with AIC.
Subcommittee meetings
The subcommittee will schedule discussions with AIC.
Support for the Subcommittee
The subcommittee will, should it wish, be provided with independent support from a person
experienced in helping negotiate and resolve conflicts. This person will not lead the discussions.
The subcommittee will, should it wish, be provided with help from the zone facilitator to set up
meetings and take notes.
The subcommittee will be able to request information from the Environment Canterbury technical
team. Such information will be provided where possible noting the tight timetable.
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AGENDA ITEM NO: 11 (i) SUBJECT MATTER:
Advice on whether implementing the HWRRP minimum flows could be deferred on consents currently being renewed
AUTHOR: Lisa Jenkins, Environment Canterbury DATE OF MEETING: 11 December 2017
Action required
1. The Zone Committee notes that implementation of HWRRP minimum flows cannot be deferred for resource users with consents which will expire prior to a comprehensive review of all water take consents.
Discussion The Hurunui Waiau Zone Committee are considering whether to recommend the review of water‐take consents so that minimum flows identified in the Hurunui Waiau Rivers Regional Plan (HWRRP) are implemented within the life of the Plan. Some water‐take consents already implement the HWRRP flow regime, while other consents will not expire until after the HWRRP is reviewed in 2023. When a consent is renewed, the new HWRRP minimum flows must be applied. The water supply becomes less reliable for irrigators subject to the new minimum flow regime. This creates a situation where some irrigators have a less reliable water supply than others. At the 20 November 2017 Zone Committee meeting, the Committee asked if it is possible for resource consent renewals to be deferred so that irrigators are not subject to the HWRRP minimum flow regime until all consents are reviewed. Once a consent is expired, the activity for which the consent was in place must cease until a new resource consent is granted. If a consent expires and is not renewed, the resource becomes available for other users to seek consent for on a first come first serve basis. Deferring renewals would not be possible as water users would be contravening the Resource Management Act if they continue to take water without consent.
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MEMORANDUM
From Peter Brown
Reviewer(s)
To Andrew Barton
Date 4 December 2017
Subject On-farm impact of irrigation restrictions
Status DRAFT
Overview • I have modelled how changing from AIC’s current minimum flows, to HWRRP minimum flows
would affect restrictions and soil moisture on-farm.
• These results have been used by Mr Mark Everest to estimate the on-farm economic impacts of
changing minimum flows.
• I have compared Mr Everest’s production loss estimates to my 2012 HWRRP hearing estimates,
and have found the two models are producing similar results.
• The main difference with the 2012 work is with the ‘status quo’ scenario for the Waiau Irrigation
Scheme. My 2012 evidence presented a generic A-Block reliability and did not model the
specifics of Amuri Irrigation’s Waiau Irrigation Scheme consent, which has higher reliability.
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River flow and restriction modelling River flow modelling and reliability given AIC’s current consents and HWRRP minimum flows, are
described in my memorandum titled “Hydrological change from implementing HWRRP minimum
flows” and dated 25 September 2017. These calculations have been reviewed by Environment
Canterbury.
Soil moisture modelling I modelled soil moisture using a FAO 56 soil water balance model. This is an internationally accepted
method for estimating irrigation water requirements and soil moisture levels. The model was
calibrated to align with previous AusFarm soil water balance modelling. I modelled two rainfall
stations, and two soils (a total of four scenarios) to capture a range of climate and soil conditions. The
two climate scenarios were Culverden (mean annual rainfall = 640mm/y) and the average of Riverside
and Waiau township (mean annual rainfall = 730mm/y). Potential evapotranspiration data was from
Culverden (annual average = 850mm/y). The period of simulation was 1 June 1960 to 31 May 2017.
Key parameters are summarised in Table 1. The soil moisture for every day of the 57 years of
simulation were provided to Mr Everest. Mr Everest used these estimates to predict the production
loss due to soil moisture stress.
Table 1. Key soil water balance model parameters
Parameter Soil 1 Soil 2
PAW (mm) 65 80
Crop coefficient 0.95 0.95
Water stress point (% PAW) 50% 50%
Application depth 20.8 20.8
Trigger soil moisture level (% PAW) 0.54 0.57
Application efficiency 80% 80%
System capacity (mm/d) 5.20 5.20
Effective application depth 16.64 16.64
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HWRRP Hurunui River hearing evidence In my supplementary evidence presented at the hearing on 5 December1, Scenarios 1 represents
Amuri Irrigation’s current consent (CRC951326.1), while Scenario 4 is very close to the current Hurunui
A-Block. These scenarios are summarised in Table 2.
Table 2: Hurunui scenarios modelled
ID 2012 Scenario HWRRP Table
1 1 4
Name Amuri HWRRP post-
storage Hurunui A-
Block
Block size 5.00 6.20 6.47
Flow sharing No No No
Minimum flow by month
Jan 12.0 15.0 15.0
Feb 12.0 15.0 15.0
Mar 12.0 15.0 15.0
Apr 12.0 15.0 15.0
May 12.0 12.0 12.0
Jun 12.0 12.0 12.0
Jul 12.0 12.0 12.0
Aug 13.0 12.0 12.0
Sep 15.0 15.0 15.0
Oct 19.0 15.0 15.0
Nov 18.0 15.0 15.0
Dec 13.5 15.0 15.0
I have extended reliability modelling to include the last 5 years. River flows, and consequently
reliability over the last 5 years has been below the long-term average. This means the average
reliability for the period 1960 to 2017 (Table 3) is slightly lower than my 2012 estimates, which were
for the period 1960 to 2012. Table 3 illustrates that reliability for Scenario 4 (2012) and the current
HWRRP Hurunui A-Block, are almost identical2.
Table 3: Hurunui A-Block reliability (expressed as % available) from 1 June 1960 to May 2017
Scenario Average year 1 yr in 10 Worst year
Sept-Apr
Oct-Mar
Sept-Apr
Oct-Mar
Sept-Apr
Oct-Mar
2012 Scenario 1 (Amuri) 95.8% 96.0% 88.3% 88.5% 60.5% 63.4%
2012 Scenario 4 (HWRRP post-storage) 90.8% 91.0% 78.5% 77.8% 55.8% 57.7%
HWRRP final 90.8% 91.0% 78.5% 77.8% 55.8% 57.7%
1 Brown (2012). “Statement of evidence of Peter Derek Brown for Canterbury Regional Council dated 5 December 2012. Supplementary evidence for the Hurunui and Waiau Regional Plan”. 65pp. Refer Paragraph 6. 2 The difference between the two scenarios is 0.01%.
55
When HWRRP minimum flows are applied to AIC’s Balmoral consent, average
supply reliability will reduce from 96.0% to 91.0% (Oct-Mar)
In my 2012 evidence I estimated the production loss due to water stress as a percentage of average
annual production. Key results are reproduced in Table 4. To convert from this metric to kg-DM/ha,
the percentages should be multiplied by the annual production. Mr Everest has estimated that
average annual pasture growth will range from 12.5 t-N/ha to 15.2 t-N/ha, depending on the amount
of nitrogen applied. Table 5Table 4 and Table 6 present the production impacts in kg-DM/ha, using
these annual production estimates.
Most of this loss will occur during, and shortly after, the period of restriction. So, while on an annual
basis the percentage lost production may appear quite low, the reduction in growth during the period
of restriction will be significantly greater.
My 2012 production loss estimates are similar to Mr Everest’s 2017 estimates. Generally, my
modelling indicated a greater impact in areas with low rainfall and light soils (particularly during dry
years), but a lesser impact on heavier soils. Overall however the two modelling approaches are
indicating a similar scheme level impact.
Table 4: Hurunui production impacts (from Brown 2012, paragraph 18)
Scenario
Farm 1 Farm 2
Average 1 yr in
10 3 worst years
Average 1 yr in
10 3 worst years
AIC CRC951326.1 (2012 Scenario 1) 1.3% 2% 15% 0.90% 1% 13%
HWRRP (2012 Scenario 4) 3.6% 11% 19% 1.30% 3% 23%
Table 5: Hurunui production impacts in kg-DM/y (Farm 1 – light soil, low rainfall)
Average 1 yr in 10 3 worst years
Annual growth (kg-DM/ha) 12500 15200 12500 15200 12500 15200
AIC current (2012 Scenario 1) 163 198 250 304 1875 2280
HWRRP (2012 Scenario 4) 450 547 1375 1672 2375 2888
Change 288 350 1125 1368 500 608
Table 6: Hurunui production impacts in kg-DM/y (Farm 2 – heavier soil, higher rainfall)
Average 1 yr in 10 3 worst years
Annual growth (kg-DM/ha) 12,500 15,200 12,500 15,200 12,500 15,200
AIC current (2012 Scenario 1) 113 137 125 152 1625 1976
HWRRP (2012 Scenario 4) 163 198 375 456 2875 3496
Change 50 61 250 304 1250 1520
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HWRRP Waiau River hearing evidence In my 2012 hearing evidence, Scenarios 1 (status quo) is the closest to represents Amuri Irrigation’s
current consent (CRC951304), while Scenario 3 (HWRRP 18cu) is very close to the current Waiau A-
Block.
Scenario “status quo” approximately describes the average reliability of the Waiau Bands 1-7 that
existed in 2012. Bands 1-7 together had a total allocation of about 18 m3/s. Bands 1-7 consents all
share the same minimum flows, but because of variations in consent conditions there are a range of
different reliability levels within this “A-Block”. AIC’s consent CRC951304 conditions can be
interpreted in different ways. In analysis I have used the interpretation from ECan’s compliance
department (refer Brown 20113). I have rerun the reliability analysis for the period 1960 to 2017 (refer
Table 7). In my 2012 evidence the period of analysis was 1968 to 2012. These two periods have slightly
different long-term reliability.
Table 7: Waiau A-Block reliability (expressed as % available) from 1 June 1960 to May 2017
Scenario Average year 1 yr in 10 Worst year
Sept-Apr
Oct-Mar
Sept-Apr
Oct-Mar
Sept-Apr
Oct-Mar
2012 Scenario 1 (status quo) 95.7% 96.9% 88.7% 90.6% 73.2% 82.4%
2012 Scenario 3 (HWRRP 18cu 94.7% 94.8% 85.6% 85.6% 69.5% 73.9%
HWRRP final (Waiau A-Block) 94.8% 94.9% 85.7% 85.8% 69.7% 74.0%
AIC (CRC951304) 97.8% 98.8% 93.7% 96.6% 80.2% 90.1%
Table 7 illustrates that there is a reasonable difference between my 2012 Scenario 1 (status quo) and
AIC’s consent CRC951304, with the latter have higher reliability.
When HWRRP minimum flows are applied to AIC’s Waiau consent, average
supply reliability will reduce from 98.8% to 94.9% (Oct-Mar)
Production loss estimates from my 2012 evidence are not directly comparable, because of the
differences between Scenario 1 and AIC’s consent CRC951304. Indicatively, production losses for
CRC951304 [due to restrictions] will be one third of Scenario 1. Results are presented below. As with
the Hurunui, the results align reasonably closely with Mr Everest’s production modelling.
3 Brown (2011). “Waiau River Irrigation Reliability”. Report prepared for Environment Canterbury by Aqualinc Research Ltd. April 2011.
57
Table 8: Waiau production impacts (from Brown 2012, paragraph 29)
Scenario
Farm 1 Farm 2
Average 1 yr in
10 3 worst years
Average 1 yr in
10 3 worst years
2012 Scenario 1 (status quo) 1.1% 4% 6% 0.20% 1% 1%
AIC CRC951326.14 0.4% 1.3% 2.0% 0.1% 0.3% 0.3%
HWRRP & 2012 Scenario 3 2.1% 6% 14% 1.00% 3% 9%
Table 9: Hurunui production impacts in kg-DM/y (Farm 1 – light soil low rainfall)
Average 1 yr in 10 3 worst years
Annual growth (kg-DM/ha) 12500 15200 12500 15200 12500 15200
AIC CRC951326.1 46 56 167 203 250 304
HWRRP & 2012 Scenario 3 263 319 750 912 1750 2128
Change 217 263 583 709 1500 1824
Table 10: Hurunui production impacts in kg-DM/y (Farm 2 – heavier soil, higher rainfall)
Average 1 yr in 10 3 worst years
Annual growth (kg-DM/ha) 12,500 15,200 12,500 15,200 12,500 15,200
AIC CRC951326.1 8 10 42 51 42 51
HWRRP & 2012 Scenario 3 125 152 375 456 1125 1368
Change 117 142 333 405 1083 1317
4 Not in 2012 evidence. Assumed to be 1/3 of Scenario 1
58
IRRIGATION RELIABILITY
Prepared for: Amuri Irrigation Company
By: Mark Everest
Date: 4 December 2017
1. Introduction This analysis has been prepared as requested by Andrew Barton and Peter Brown of Amuri Irrigation Company (AIC) to assess the potential on farm impacts of changing minimum flows in the Hurunui and Waiau rivers under the HWRRP. The report looks only at pasture impacts of varied minimum flow takes. The two pastoral types considered are “Dairy” and “Non-Dairy”, used to represent very intensive and intensive land uses respectively.
2. Summary The average loss of yield forecasted for dairy is:
Hurunui river: 203kgDM/ha/year (at an average cost of $97/ha/year) Waiau river: 108kgDM/ha/year (at an average cost of $52/ha/year) The worst seasons are likely to see a reduction in yield that would cost $323/ha/year on the Hurunui River and $435/ha/year on the Waiau River. (approximately 10% of the EBITDA on a very well run, property).
The average loss of yield forecasted for non-dairy is:
Hurunui river: 196kgDM/ha/year (at an average cost of $78/ha/year) Waiau river: 105kgDM/ha/year (at an average cost of $42/ha/year) The worst seasons are likely to see a reduction in yield that would cost $323/ha/year on the Hurunui River and $351/ha/year on the Waiau River. (approximately 20% of the EBITDA on a very well run property).
The average increase of regrassing required due to water-limited death of pastures is forecasted to increase by: Hurunui river: 6.8% of farm area (at an average cost of ($123/ha/year) Waiau River: 4.6% of farm area (at an average cost of ($83/ha/year)
The worst seasons are likely to see irreparable damage to pastures that would cost an average of $583/ha on the Hurunui River and $566/ha on the Waiau River. (approximately 14% of the EBITDA on a very well run dairy property, or 26% of the EBITDA on a very well run non-dairy property).
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Grain feeding:
To cost of installing grain feeders is estimated at approximately $347/ha, with an annual interest and depreciation cost of $39/ha. This would only apply to those farmers that don’t already have in-shed grain feeding facilities. We estimate that 30% of properties would need to install in-shed grain feeding facilities.
When looking at the results it is important to consider that while the average of the time period does not incur significant cost relative to the worst seasons, 41% of the time in the Hurunui River catchment, and 14% of the time in the Waiau River catchment will incur pasture damage greater than 5% more than the current low flow regime If is not the hard years alone that cost, but also the psychological effect on farmers ability to perform at historical in subsequent seasons. The stress of having to feed much more and re-grass more of the farm, bring in more feed, and in all reality drop production and profitability, in my experience often leads to a more conservative operator for the two subsequent seasons. Feed costs assumed are long run average. While some operators would hold feed on hand awaiting a time when it is required, most will go to the market at the time which can cause inflated costs, especially in a semi-isolated area like the Amuri. This can mean silage cost can increase to 25c/kgDM standing in the paddock and grain may increase in cost by a further $50/t.
3. Process Using soil moisture models as provided by Peter Brown, I have looked at the effects on growth rate of pasture on a daily time step model across both Waiau and Hurunui rivers, and assessed the river flow regimes across two soils (65mm profile available water and 80mm profile available water) and rainfall zones (Culverden and Riverside/Waiau). The time period assessed is from 1960 to 2017. The daily time step model calculates potential growth based on expected pasture growth (from an internal MRB data set and external industry data) assuming no irrigation restriction, plus nitrogen effect, less soil moisture stress impact on pasture production. Growth rate and nitrogen assumptions are below:
Un-boosted N units N Boosted
June 8 0 8
July 4 0 4
August 12 7 15
September 23 29 35
October 39 35 52
November 65 14 69
December 74 0 74
January 63 0 63
February 51 35 65
March 38 24 47
April 22 6 24
May 18 0 18
TOTAL 12,531 149 14,221
PASTURE GROWTH - PASTORAL (non dairy)
un boosted N units N Boosted
June 8 0 8
July 4 0 4
August 12 14 18
September 23 28 34
October 39 39 53
November 65 36 77
December 74 28 83
January 63 28 72
February 51 33 64
March 38 27 48
April 22 15 28
May 18 0 18
TOTAL 12,531 247 15,218
PASTURE GROWTH - PASTORAL (dairy)
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Once the lost potential feed was calculated (on an annual basis), the cost to the business was calculated. It is assumed that the “dairy” would buy in grain and baleage to replace pasture not grown. PKE was excluded from analysis as the amount that is permitted to be fed currently is only 3kgDM, also there is risk that it will become a banned product for use in some markets in future. The replacement feed costs for the “dairy” type systems are detailed below:
It is assumed that the “non-dairy” represents other enterprises including beef fattening, lamb finishing, dairy grazing and silage sales. These enterprises would likely employ a combination of selling stock that they could have added more weight to, not trading stock as they don’t have the feed, and buying in feed. The bought in feed would be all pasture silage except some grain for breeding ewes or lambs, which would free up pasture for other grazing cattle. The replacement feed costs and finishing/grazing margin reductions for “non-dairy type systems are detailed below:
Grain: $380 /t delivered
86% dry matter
$442 /tDM delivered
$20 /tDM to crush and feed
98% ulilisation
$471 /tDM consumed
Baleage: $180 /tDM standing
$144 /tDM mow, bale and wrap ($46/320kgDM)
$31 /tDM to cart ($10/320kgDM)
$56 /tDM to feed ($18/320kgDM)
85% ulilisation
$484 /tDM consumed
AVERAGE $478 /tDM consumed
FEED COSTS - PASTORAL (dairy)
Grain: (20%) $380 /t delivered
86% dry matter
$442 /tDM delivered
$20 /tDM to feed
80% ulilisation
$577 /tDM consumed
Baleage: (40%) $180 /tDM standing
$144 /tDM mow, bale and wrap ($46/320kgDM)
$31 /tDM to cart ($10/320kgDM)
$56 /tDM to feed ($18/320kgDM)
85% ulilisation
$484 /tDM consumed
Lost Margins: (40%) $180 /tDM Lamb Finishing
$278 /tDM Calf Trading
$197 /tDM R2 Finishing
$218 /tDM consumed
AVERAGE $396 /tDM consumed
FEED COSTS - PASTORAL (non dairy)
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4. Results Non-Dairy - Pasture Yield
The MAX yield represents the best year in the data set from 1960 to 2017, the MIN yield represents the worst year (the most expensive year for a farmer under the HWRRP regime in comparison to current) and the AVERAGE yield is the average of all of the seasons.
Rainfall
Soil PAW (mm)
Minimum flow Current HWRRP Current HWRRP Current HWRRP Current HWRRP
MAX Yield (KgDM/ha/yr) 14,429 14,429 14,429 14,429 14,429 14,427 14,429 14,429
(HWRRP % Currrent) 100.0% 100.0% 100.0% 100.0%
(Yield Loss kgDM/ha/yr) 0 0 3 0
(Cost of bought in feed/ha/yr) $0 $0 $1 $0
MIN Yield (KgDM/ha/yr) 12,019 11,327 12,108 11,449 12,080 11,444 12,161 11,592
(HWRRP % Currrent) 94.2% 94.6% 94.7% 95.3%
(Yield Loss kgDM/ha/yr) 691 659 637 569
(Cost of bought in feed/ha/yr) $274 $261 $252 $225
AVERAGE Yield (KgDM/ha/yr) 14,190 13,968 14,239 14,041 14,227 14,032 14,265 14,095
(HWRRP % Currrent) 98.4% 98.6% 98.6% 98.8%
(Yield Loss kgDM/ha/yr) 222 197 195 171
(Cost of bought in feed/ha/yr) $88 $78 $77 $68
HURUNUI RIVER - PASTORAL (non-dairy)
Culverden Riverside and Waiau
65 80 65 80
Rainfall
Soil PAW (mm)
Minimum flow Current HWRRP Current HWRRP Current HWRRP Current HWRRP
MAX Yield (KgDM/ha/yr) 14,429 14,429 14,429 14,429 14,429 14,427 14,429 14,429
(HWRRP % Currrent) 100.0% 100.0% 100.0% 100.0%
(Yield Loss kgDM/ha/yr) 0 0 3 0
(Cost of bought in feed/ha/yr) $0 $0 $1 $0
MIN Yield (KgDM/ha/yr) 13,992 12,892 14,113 13,269 14,071 13,196 14,152 13,424
(HWRRP % Currrent) 92.1% 94.0% 93.8% 94.9%
(Yield Loss kgDM/ha/yr) 1100 844 876 728
(Cost of bought in feed/ha/yr) $436 $334 $347 $288
AVERAGE Yield (KgDM/ha/yr) 14,302 14,182 14,334 14,230 14,326 14,216 14,351 14,264
(HWRRP % Currrent) 99.2% 99.3% 99.2% 99.4%
(Yield Loss kgDM/ha/yr) 120 104 110 87
(Cost of bought in feed/ha/yr) $48 $41 $43 $34
WAIAU RIVER - PASTORAL (non-dairy)
Culverden Riverside and Waiau
65 80 65 80
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Dairy – Pasture Yield
Rainfall
Soil PAW (mm)
Minimum flow Current HWRRP Current HWRRP Current HWRRP Current HWRRP
MAX Yield 15,450 15,450 15,450 15,450 15,450 15,447 15,450 15,450
(HWRRP % Currrent) 100.0% 100.0% 100.0% 100.0%
(Yield Loss kgDM/ha/yr) 0 0 3 0
(Cost of bought in feed/ha/yr) $0 $0 $1 $0
MIN Yield 12,985 12,249 13,072 12,378 13,041 12,364 13,119 12,522
(HWRRP % Currrent) 94.3% 94.7% 94.8% 95.5%
(Yield Loss kgDM/ha/yr) 736 694 677 597
(Cost of bought in feed/ha/yr) $352 $331 $323 $285
AVERAGE Yield 15,201 14,971 15,253 15,048 15,240 15,038 15,282 15,105
(HWRRP % Currrent) 98.5% 98.7% 98.7% 98.8%
(Yield Loss kgDM/ha/yr) 230 204 202 176
(Cost of bought in feed/ha/yr) $110 $98 $97 $84
HURUNUI RIVER - PASTORAL (dairy)
Culverden Riverside and Waiau
65 80 65 80
Rainfall
Soil PAW (mm)
Minimum flow Current HWRRP Current HWRRP Current HWRRP Current HWRRP
MAX Yield 15,450 15,450 15,450 15,450 15,450 15,447 15,450 15,450
(HWRRP % Currrent) 100.0% 100.0% 100.0% 100.0%
(Yield Loss kgDM/ha/yr) 0 0 3 0
(Cost of bought in feed/ha/yr) $0 $0 $1 $0
MIN Yield 14,999 13,852 15,118 14,252 15,079 14,171 15,163 14,438
(HWRRP % Currrent) 92.4% 94.3% 94.0% 95.2%
(Yield Loss kgDM/ha/yr) 1147 866 908 725
(Cost of bought in feed/ha/yr) $548 $413 $434 $346
AVERAGE Yield 15,316 15,192 15,351 15,244 15,341 15,228 15,369 15,280
(HWRRP % Currrent) 99.2% 99.3% 99.3% 99.4%
(Yield Loss kgDM/ha/yr) 124 107 113 89
(Cost of bought in feed/ha/yr) $59 $51 $54 $42
WAIAU RIVER - PASTORAL (dairy)
Culverden Riverside and Waiau
65 80 65 80
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Increased Regrassing The MAX increased regrassing represents the worst year in the data set from 1960 to 2017 (the most expensive year for a farmer under the HWRRP regime in comparison to current), the MIN increased regrassing represents the best year, and the AVERAGE yield is the average of all of the seasons. The cost of regrassing includes the cost of supplementary feed bought in to replace the pasture not growing at the time of regrassing (assumed at 60 days from first spray out to first grazing). The pasture not grown is assumed as the average growth rate over that time, less the dry matter made available to first grazing in the new grass.
Rainfall
Soil PAW (mm)
Years % area Years % area Years % area Years % area
HWRRP more than Current regrassing 31 54% 30 53% 30 53% 30 53%
MAX increased regrassing 32% 32% 32% 33%
Estimated cost (per ha in worst year) $577 $569 $583 $602
MIN increased regrassing 0% 0% 0% 0%
Estimated cost (per ha in worst year) $0 $0 $0 $0
AVERAGE increased regrassing 7% 7% 7% 7%
Estimated cost (per ha in worst year) $118 $127 $123 $124
HURUNUI RIVER - PASTORAL (Regrassing Required - non-dairy and dairy)
Culverden Riverside and Waiau
65 80 65 80
Rainfall
Soil PAW (mm)
Years % area Years % area Years % area Years % area
HWRRP more than Current regrassing 22 39% 26 46% 24 42% 24 42%
MAX increased regrassing 29% 30% 33% 33%
Estimated cost (per ha in worst year) $521 $547 $601 $593
MIN increased regrassing 0% 0% 0% 0%
Estimated cost (per ha in worst year) $0 $0 $0 $0
AVERAGE increased regrassing 4% 5% 5% 5%
Estimated cost (per ha in worst year) $72 $91 $87 $82
WAIAU RIVER - PASTORAL (Regrassing Required - non-dairy and dairy)
Culverden Riverside and Waiau
65 80 65 80
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Cost of Grain Feeding The cost of retrofitting a rotary dairy shed (60 bail) with a grain feeding system (180t silo, mill, hopper silo, PLC, and feed bins is approximately $80,000. This would be suitable for a 230ha or 800 cow farm, making the capital cost approximately $347/ha in capital. There would be: an interest bill on the borrowed money at 7.25%: $25/ha/year
depreciation over a 25 year lifespan: $14/ha/year TOTAL $39/ha/year
This cost if farm specific – it does vary greatly by property and would only affect the farmers that do not already feed grain in milking sheds.
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AGENDA ITEM NO: 12 SUBJECT MATTER:
Wilding conifer strategy and action in the zone
AUTHOR: Ian Whitehouse, Environment Canterbury
DATE OF MEETING: 11 December 2017
Action required
1. Note the Wilding Conifer Management Strategy 2015 – 2030 (copies will be available at the
meeting);
2. Note the South Island Wilding Conifer Programme 2016/17 and 2017/2018 (attached);
3. Alan Tinnelly, Ministry for Primary Industries, will brief the committee on the strategy and
wilding conifer programme in the zone.
Background
The National Wilding Conifer Control Programme is looking to liaise with bodies such as the Zone
Committees to support greater awareness of the wilding problem and the national control
programme. This issue is most significant in, but not restricted to, the central high‐country tussock
grasslands of New Zealand.
Losses for NZ’s primary production, water availability, tourism and environment is significant if
wildings are not controled. Wildings impact on our valuable water yields. In small catchment studies
water yields can be reduced by over 50% when native tussock is replaced by conifers. A study at
Glendu identified that water yields were reduced by 42%. A further study undertaken by NIWA on
the Waitaki River catchment estimated a reduction of up to 50 cumec if conifers were left
uncontrolled. This reduction would severely reduce on the number of days farmers could irrigate,
less water yield with constant contaminant discharges which would potentially lower water quality.
A reduction in power generation and as bigger areas of dense wilding conifers the impacts of wild
fires also increases.
Wilding conifers are a serious and increasing pest issue for New Zealand. Over 2 million hectares,
around 6% of New Zealand, have already been affected to some extent by these unwanted trees.
Wilding conifers are continuing to increase in area at an average compounding rate of approximately
5‐6% per year. At this rate of spread within 20‐30 years wilding conifers will have invaded (and have
reached at least medium densities) approximately 5.9 million hectares (22% of New Zealand’s total
land area) of at risk land. In addition, a proportion of indigenous forests, including beech forest and
Manuka/Kanuka forests, which represent an additional 24% of total land cover, will be invaded over
a longer period of time.
Wilding conifers are an issue that can only be addressed by landowners, forest owners, community
groups, industry researchers, local and central government working together. The New Zealand
Wilding Conifer Management Strategy 2015‐2030 (the strategy) aims to support effective
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collaboration between land occupiers, researchers, regulators and communities to address the
critical overarching issues facing wilding conifer management.
As part of the strategy’s implementation Government announced in Budget 2016 a contribution of
$16 million over 4 years for a collaborative national wilding conifer control programme.
The allocation of funds for each programme year is agreed at a national Governance Group level.
The regional steering groups, of which the regional fund‐holder (ECan in Canterbury) is a member,
are responsible for providing oversight of the operational programme in their respective region(s).
The 2016 / 2017 operational programme made a significant dent in targeting outlying infestations of
over 1.2 m/ha of affected land covering 14 management units though out the country. The focus for
operational control over a 3 year programme is depicted in the attached map.
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U:\2017\C17070J_PCa_Wilding_Conifer_Mgmt_Unit_Mapping\GIS\C17070_003_A3P_SouthIsland_Affecte
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Northern Eyre
Mid Dome
St Mary-Ida
Remarkables
Five RiversLammermoor
Ohau
Tekapo East
Tekapo West
Kawarau
Godley
Craigieburn
Dunstan
Four Peaks
Lewis
Molesworth
Hakatere
Porters
SouthlandRegion
Otago
Region
CanterburyRegion
West CoastRegion
TasmanRegion
MarlboroughRegion
NelsonRegion
TaranakiRegion
Te WaipounamuSouth Island
AotearoaNew Zealand
INVERCARGILL
Queenstown
Balclutha
OAMARU
Waimate
TIMARU
Hokitika
Greymouth
ASHBURTON
Reefton
Akaroa
Kaikoura
NELSON
Motueka
BLENHEIM
Picton
Opunake
Hawera
NEW PLYMOUTH
DUNEDIN
CHRISTCHURCH
WELLINGTON
NATIONAL WILDING CONIFER PROGRAMME
Legend
Regional Council Boundary
Management Unit Commenced 2016/17
Management Unit Commenced 2017/18
Wilding Conifer Affected Areas
°Data AcknowledgementMaps contain data sourced from LINZ. Crown Copyright Reserved
0 100 km
1:2,400,000 @ A3
South Island Management Units
Management Unit Unit ID Area (ha)
Molesworth MU41-01 231,610Lewis MU35-01 298,757Craigieburn MU34-02 201,291Porters MU34-01 200,799Hakatere MU32-03 345,978Godley MU32-02 137,921Four Peaks MU32-01 39,725St Mary-Ida MU24-01 355,638Dunstan MU23-02 108,102Kawarau MU21-03 56,046Remarkables MU21-02 111,061Northern Eyre MU21-01 107,237Five Rivers MU11-01 9,853TOTAL 2,204,018
Tekapo West MU32-07 91,720Tekapo East MU32-06 108,716Ohau MU32-04 309,518Lammermoor MU23-01 258,430Mid Dome MU11-02 64,064TOTAL 832,448
Management Unit Commenced 2017/18
Management Unit Commenced 2016/17
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AGENDA ITEM NO: 9 SUBJECT MATTER: Zone Facilitator’s Report
REPORT BY: Ian Whitehouse, Environment Canterbury
DATE OF MEETING: 16 October 2017
Action required
1. Identify and prioritise, if required, existing/new initiatives and/or work programmes that the
Committee considers should be provided for in the Environment Canterbury 2018‐2028 Long
Term Plan (LTP).
2. Identify what should be included in the “Key achievements 2017” section of the Zone Committee Annual Report 2017 and the projects/initiatives that could feature on page 2 of the report.
3. Note the proposed water quality (E. coli) monitoring programme for 2017/18 summer above SH7 on Hurunui River.
4. Note the publication of the CWMS Targets Progress Report 2017. 1 Input to Environment Canterbury LTP Environment Canterbury’s Long Term Plan (LTP) sets out the Council’s service priorities, work programmes and resource requirements such as expenditure and funding for a 10‐year period. A new Long‐Term Plan is produced every three years, which incorporates the Annual Plan for that year. In June 2018 a new LTP (for 2018‐2028) will be adopted by the Environment Canterbury Council. Environment Canterbury is currently seeking input from stakeholders on the strategic direction of Environment Canterbury. Environment Canterbury is inviting feedback from all 10 zone committees. A clear message has been given to Environment Canterbury that the priorities for the coming years must be water management and native biodiversity. The zone committee has written to Environment Canterbury (see “Correspondence”) asking for some of the savings from the targeted approach in Hurunui Waiau to be redirected to on‐the‐ground work programmes in the zone including, though not limited to, conservation management of braided river beds. What existing/new solutions does the Committee consider should be provided for in the Environment Canterbury 2018‐2028 LTP to deliver on the Freshwater management and Indigenous biodiversity priorities in the Hurunui Waiau Zone? 2 Zone Committee’s 2017 Annual Report The committee’s Annual Report for 2017 will be signed off at the first meeting in 2018. The Annual Report forms the basis for the Chair reporting to Hurunui District councillors and to Environment Canterbury councillors. The 2016 Annual Report is attached. Committee members are asked to identify the things that they believe should be included in the “Key achievements 2017” section (for example AIC piping, allocating over $300,000 of Immediate Steps Biodiversity funding to braided river projects).
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Committee members are asked to suggest the projects/initiatives that will feature on page 2 of the Zone Committee’s 2017 Annual Report. 3 Further water quality (E. coli) monitoring in Hurunui River above SH7 Results from the monitoring in 2016/17 summer were presented and discussed at the September meeting. The committee asked Environment Canterbury to come back with a proposal for further monitoring in the 2017/18 summer. The proposed monitoring is described in the attached paper. 4 CWMS Targets Progress Report 2017
The ten CWMS target areas and the specific goals within these for 2015, 2020 and 2040 are a critical
part of implementing the CWMS. Environment Canterbury has provided progress reports, since
2012, on the achievement of the targets.
The CWMS Targets Progress Report 2017 has just been completed – see
https://www.ecan.govt.nz/your‐region/your‐environment/water/measuring‐progress/
Printed copies will be available at the meeting.
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Attachment to Zone Facilitator’s Report
Proposed further water quality (E.coli) monitoring in Hurunui above SH7 for summer 2017/18
Following the discussion of results from E.coli monitoring at multiple sites in the Hurunui River above
SH7 at the last Zone Committee meeting (18 September 2017), the Committee asked the
Environment Canterbury technical team to come back with options to further investigate this issue
over the coming 2017/18 summer. The Committee was particularly interested in now narrowing the
investigation to try and identify what might be causing the consistently elevated E.coli results found
in the lower part of the study reach (i.e., around Lower River Rd and at SH7). In response the
technical team suggest a three‐pronged approach for the coming summer season:
1. A one‐day visual survey (on foot) of the reach of riverbed between Hocking Rd and SH7
during October‐November 2017 to identify presence and type of bird colonies and any other
potential sources of E.coli evident from the riverbed.
2. A weekly E.coli sampling programme similar to the 2016‐17 Hurunui programme (i.e.
coinciding with ECan’s regular recreational water quality programme) but narrowing in on
the Lower River Rd site and up to two other sites in addition to the regular SH7 site. The
additional sites will be selected following the foot survey mentioned above.
3. Sub‐samples from each location and date will be stored (frozen) until the end of summer to
retain the option of sending some high E.coli yielding samples to the ESR lab for faecal
source tracking analysis, to try and distinguish between animal sources.
In addition, Mayor Winton Dalley asked if staff could confirm whether the high flow event seen on
14 February 2017 coinciding with high E.coli concentrations in the results presented for last summer
was the result of rain in the hills, on the plains or both. The graph below shows river flow and rainfall
around 14 February 2017 and confirms that the high flow event was an alpine‐fed event apparently
without significant contribution from rain on the plains. This raises the question of what sources
caused the high E.coli results on 14 February 2017 at all sites below Morrisons Rd and whether rising
water levels may have contributed by washing faeces from bird colonies. However, this idea does
not explain the consistently elevated E.coli results throughout the summer at low flows at the Lower
River Road site or the poor quality measured at SH7 which is only graded under stable flow
conditions. The results to date show that both ruminant animals and birds contribute to E.coli
measured at SH7 but the exact source location(s) and relative proportions of these contributions
remain unclear.
River flow and rainfall patterns will be taken into account in analysing the results from the proposed
summer 2017/18 study described above.
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Waiau river bird survey 2017 summary The Waiau River is known to be a habitat of outstanding significance for threatened native birds. It has been shown to support the northern‐most known breeding population of wrybill as well as internationally significant populations of black‐fronted terns and black‐billed gulls, and a regionally significant population of banded dotterel. This is the sixth year of surveying. In 1975 the sections from Twin Bridges to Sandersons Road were covered (our sections 4‐8), and in 2008, 2009, 2010, and 2016 the survey has covered the river from Waterfall Stream to the river mouth (15 sections), see Map 1 below. Typically the braided river bird surveys are undertaken in three‐year blocks, scheduled to repeat every five years. The survey scheduled to happen in 2015 was postponed until 2016, meaning that there is one year of surveying to occur in 2018 to complete this cycle. In support of the Hurunui‐Waiau Braided Rivers Flagship Immediate Steps Project an additional three years of surveying is proposed and it is also proposed that this is led by Environment Canterbury, how this will occur is still yet to be confirmed. In 2017 the Environment Canterbury led bird survey of the Waiau River ran over four days from October 17th to 20th. Thirty participants took part in the survey, covering over 100KM of riverbed from the Waterfall Stream starting point, through the gorges to the river mouth. Conditions were generally good, with only one day having some rain in the morning. This winter’s high rainfall has cleared the river up quite a bit, but this also meant the river flow was quite high and the cloudiness of the water made it difficult for the boat drivers to assess depth so they had to take extra care in choosing pick up and drop off points. Data from the survey will be shared with the local braided river bird advocacy group BRaid and the Department of Conservation, who collates all braided river bird count datasets. These datasets provide important information on the use of the river by the bird species, informing river management decisions and agency resourcing of conservation activities. Key observations from 2017
Numbers were slightly lower than last year for wrybill, banded dotterel and black fronted tern, however, the black billed gull numbers were higher than they have been since 2008.
One black billed gull colony of around 1000 birds was found. This was in section 8 which is dark green on the map.
As with last year, a colony of about 100 black‐fronted terns was located at the Shark’s Tooth upstream of Twin Bridges (section 3 = orange on the map).
Black‐backed gulls were still high but slightly less than last year.
Black‐fronted dotterel were seen again this year. Last year was the first time they had been recorded on the Waiau although they are often seen to the south at Mata Kopae / St Anne’s Lagoon and paddocks around Cheviot.
Sections 1 (red on the map), 4 (yellow) and 12 (orange) of the river seem to be favoured by river birds with these sections having the highest overall number of birds seen.
Wrybill, banded dotterel, black‐billed gull, black‐fronted tern, South Island pied oystercatcher and pied stilt are all on the threatened species list.
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Figure 1: Maps illustrating the total number of Southern black‐backed gull, black billed gull, banded dotterel, black‐fronted tern, South Island pied oystercatcher and wrybill observed during the Waiau river bird survey over five survey years.
0
500
1000
1500
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2500
2008 2009 2010 2016 2017
Black‐billed gull
0
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2000
3000
4000
5000
2008 2009 2010 2016 2017
Southern black‐backed gull
0
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2008 2009 2010 2016 2017
Black‐fronted tern
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2008 2009 2010 2016 2017
Wrybill
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2008 2009 2010 2016 2017
Banded dotterel
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2008 2009 2010 2016 2017
South Island pied oystercatcherNumber of braided
river birds observed
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Figure 2: River flow data, the survey occurred from the 17th‐20th October. The river showed evidence of recent high flows with areas of bank being washed away in some areas. The cloudiness of the water was also evidence of recent high flows.
Map 1: Showing the sections of the river that we covered. The different colours denote a day’s work (therefore, red and orange are day one for the two survey groups, yellow and green are day two etc).
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Terms of ReferenceThe area of the Hurunui Waiau Water Management Zone is shown on the attached map.
Establishment
The Committee is established under the auspices of the Local Government Act 2002 in accordance with the Canterbury Water Management Strategy 2009.
The Committee is a joint Committee of Environment Canterbury (the Regional Council) and Hurunui District Council (the Territorial Authority).
Purpose and Functions
The purpose and function of the Committee is to:
• Facilitate community involvement in the development, implementation, review and updating of a Zone Implementation Programme that gives effect to the Canterbury Water Management Strategy in the Hurunui Waiau area; and
• Monitor progress of the implementation of the Zone Implementation Programme.
Objectives
1) Develop a Zone Implementation Programme that seeks to advance theCWMS vision, principles, and targets in the Hurunui Waiau Zone.
2) Oversee the delivery of the Zone Implementation Programme.
3) Support other Zone Implementation Programmes and the Regional Implementation Programme to the extent they have common areas of interest or interface.
4) Ensure that the community of the Zone are informed, have opportunity for input, and are involved in the development and delivery of the Hurunui Waiau Implementation Programme.
5) Consult with other Zone Water Management Committees throughout the development and implementation of the Hurunui Waiau Implementation Programme on matters impacting on other zone areas.
6) Engage with relevant stakeholders throughout the development of the Hurunui Waiau Implementation Programme.
7) Recommend the Hurunui Waiau Implementation Programme to their respective Councils.
8) Review the Implementation Programme on a three yearly cycle and recommend any changes to the respective Councils.
9) Monitor the performance of Environment Canterbury, Hurunui District Council, and other agencies in relation to the implementation of the Hurunui Waiau Implementation Programme.
10) Provide Environment Canterbury and Hurunui District Council with updates on progress against the Zone Implementation Programme.
Hurunui Waiau Zone Water Management Committee
Brought to you by Environment Canterbury working with
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Limitation of Powers
The Committee does not have the authority to commit any Council to any path or expenditure and its recommendations do not compromise the Councils’ freedom to deliberate and make decisions.
The Committee does not have the authority to submit on proposed Resource Management or Local Government Plans.
The Committee does not have the authority to submit on resource consent matters.
Committee Membership
The Zone Committee will comprise:
1) One elected member or Commissioner appointed by Environment Canterbury;
2) One elected member appointed by each Territorial Authority operating within the Zone Boundary;
3) One member from each of Tūāhuriri and Kaikōura Rūnanga;
4) Between 4-7 members appointed from the community and who come from a range of backgrounds and interests within the community;
5) Environment Canterbury and Hurunui District Council will appoint their own representatives on the Committee. Tūāhuriri and Kaikōura Rūnanga will nominate their representatives and the appointments will be confirmed by Environment Canterbury and Hurunui District Council.
Selection of Community Members
To be eligible for appointment to a Zone Committee the candidate must either live in or have a significant relationship with the zone. Recommendations on Community Members for the Hurunui Waiau Zone Committee will be made to Environment Canterbury and Hurunui District Council by a working group of representatives from Environment Canterbury, Hurunui District Council, Tūāhuriri and Kaikōura Rūnanga. The recommendations will take into account the balance of interests required for Hurunui Waiau, geographic spread of members and the ability of the applicants to work in a collaborative, consensus-seeking manner. Environment Canterbury and Hurunui District Council will receive the recommendations and make the appointments.
Quorum
The quorum at a meeting consists of:
(i) Half of the members if the number of members (including vacancies) is even; or
(ii) A majority of members if the number of members (including vacancies) is odd.
Chair and Deputy Chair
Each year, the Committee shall appoint the Chair and Deputy Chair from the membership by simple majority. There is no limit on how long a person can be in either of these positions.
Term of Appointment
Members of Committees are appointed for a term of three years. To coincide with Local Government Election processes terms shall commence from January each year, with each Committee requiring confirmation of membership by the incoming Council. The term for community members will be staggered so that one third of the community members is appointed (or reappointed) each year. There is no limit on the number of consecutive terms.
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Financial Delegations
None
Operating Philosophy
The Committees will at all times operate in accordance with the requirements of the Local Government Official Information and Meetings Act 1987, and will observe the following principles:
1) Give effect to the Fundamental Principles, Targets and goals of the CWMS;
2) Be culturally sensitive observing tikanga Maori;
3) Apply a Ki uta ki tai (from the mountains to the sea) approach;
4) Work with the CWMS Regional Committee to support the implementation of the CWMS across the region as a whole;
5) Give consideration to and balance the interests of all water interests in the region in debate and decision-making;
6) Work in a collaborative and co-operative manner using best endeavours to reach solutions that take account of the interests of all sectors of the community;
7) Contribute their knowledge and perspective but not promote the views or positions of any particular interest or stakeholder group;
8) Promote a philosophy of integrated water management to achieve the multiple objectives of the range of interests in water;
9) Seek consensus in decision-making where at all possible. In the event that neither unanimous agreement is able to be reached nor a significant majority view formed, in the first instance seek assistance from an external facilitator to further Committee discussions and deliberations. Where the Committee encounters fundamental disagreements, despite having sought assistance and exhausted all avenues to resolve matters, recommend that the respective Councils disband them and appoint a new Committee.
Meeting and Remuneration Guidelines
1) The Committee will meet at least eight times per annum and with workshops and additional meetings as required. At times, the workload will be substantially higher. Proxies or alternates are not permitted.
2) Any Committee may co-opt such other expert or advisory members as it deems necessary to ensure it is able to achieve its purpose. Any such co-option will be on a non-voting basis.
3) Remuneration for members will be paid in the form of an honorarium currently set at the following levels:
a. Appointed members - $4,000 pab. Deputy Chair - $5,000 pac. Chair - $6,000 pa.
Staff or elected members of Territorial Authorities or the Environment Canterbury shall not be eligible for remuneration.
Mileage will be reimbursed.
Committee Support
The Committee shall be supported staff from the Territorial Councils and Environment Canterbury, primarily through the Committee Secretary and the Zone Facilitator.
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Map showing Hurunui Waiau Water Management
Brought to you by Environment Canterbury working with
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