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Hearing Evidence – Brunner - Federated Farmers

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BEFORE THE West Coast Regional Council<br />

IN THE MATTER OF submission on Proposed<br />

Regional Land and Water<br />

Plan 2010<br />

STATEMENT OF EVIDENCE ON BEHALF OF THE WEST COAST PROVINCE OF<br />

FEDERATED FARMERS OF NEW ZEALAND


Introduction<br />

1. My name is Katie Milne, I am the President of the West Coast Province of <strong>Federated</strong><br />

<strong>Farmers</strong> of New Zealand. I am also a Rotomanu dairy farmer, and am directly affected<br />

by the decisions of the Council that pertain to farms in the Lake <strong>Brunner</strong> Catchment.<br />

2. With me is Michael Bennett, a <strong>Federated</strong> <strong>Farmers</strong> Policy Advisor. Michael holds a BSc.<br />

degree from the University of Canterbury and an M.Com. (agricultural) degree from<br />

Lincoln University. He previously worked at Environment Southland and has 4 years of<br />

experience as a policy planner. Previous to this he undertook research on farmer<br />

perceptions of sustainability and decision making around cow wintering.<br />

3. With me also is Dave Becker from Ray White Real Estate. Dave is a licensed rural<br />

sales consultant and we have him to join us today because he has insights and<br />

experience relating to the effect of the proposed plan on the marketability and certainty<br />

of value of farms in the <strong>Brunner</strong> Catchment.<br />

Summary of <strong>Federated</strong> <strong>Farmers</strong> position<br />

4. <strong>Federated</strong> Farmer’s position is that the proposed Land and Water Plan, with<br />

amendments sought in our submission, is a good response to the management of land<br />

and water resources on the West Coast, and in particular the minor issues now being<br />

observed in Lake <strong>Brunner</strong>.<br />

5. We see the relief sought in our submission as reasonable and moderate, particularly in<br />

light of the good state of Lake <strong>Brunner</strong>, lack of evidence that farming activities are the<br />

driver of changes, widespread support for voluntary farm plans by farmers, as well as<br />

our support for practical and effective regulatory options such as stock exclusion, use<br />

of culverts and bridges, and improved farm dairy effluent management.<br />

6. Above all we do not want to jump the gun or over-complicate the situation by acting in<br />

haste. As the data set becomes more complete, the picture as to the nature of the<br />

problem and what might be required to address it will become clearer.<br />

7. <strong>Federated</strong> <strong>Farmers</strong> also has every confidence in West Coast Regional Council to<br />

continue to work proactively with farmers to manage water quality in farming<br />

catchments, and appreciates the consultative planning approach taken to minimise<br />

unnecessary confusion, uncertainty, and cost in developing this plan.<br />

Scope of evidence<br />

8. This statement of evidence is intended to support the points raised on our submission.<br />

9. The remainder of our evidence comprises:<br />

1. The issue of water quality in Lake <strong>Brunner</strong>;<br />

2. Economic and social implications for Lake <strong>Brunner</strong> farmers and the wider<br />

region;<br />

3. The proposed policy framework for the Lake <strong>Brunner</strong> catchment;<br />

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4. Other matters<br />

1. The issue of water quality in Lake <strong>Brunner</strong><br />

10. Monitoring and information on the lake indicate that <strong>Brunner</strong> is in very good condition<br />

with a very gradual declining trend. The following comments from the SOE Report are<br />

relevant:<br />

Water quality monitoring in Lake <strong>Brunner</strong> began in the early 1990s. From this data<br />

set, trends in some variables indicated that the water quality of Lake <strong>Brunner</strong> had<br />

deteriorated from 1994 to 2011, although water quality in the lake is still relatively<br />

good. (page 45)<br />

Predictive modelling estimated that phosphorus inputs into the lake would need to<br />

increase by 70 % to shift the lake into mesotrophic status. (page 45)<br />

Lake SPI analysis suggests that there has not been any change in aquatic plant<br />

community composition since 1982, hence water quality has not deteriorated<br />

sufficiently to alter them (Figure 4.2). (page 47)<br />

11. We would also like to clarify that water quality monitoring in Lake <strong>Brunner</strong> has shown<br />

highly variable results over time, with a slight, but statistically significant trend. A<br />

statistically significant reduction does not however mean that the condition of the Lake<br />

has undergone a major change or loss of value. The variability in water quality data is<br />

also typical of other lakes on the West Coast.<br />

12. The SOE Report also notes that flushing by high rainfall and the limnology of the lake<br />

provide further protection in that the thermocline established in summer and<br />

consolidation of P in lake sediments reduces vulnerability to flipping. This makes Lake<br />

<strong>Brunner</strong> unlike other, more vulnerable lakes such as Ellesmere/Te Waihora and The<br />

Waituna Lagoon.<br />

13. From the available information, <strong>Federated</strong> <strong>Farmers</strong> has concluded that Lake <strong>Brunner</strong> is<br />

not at threat of ecological change or harm, is inherently resilient, and that therefore<br />

there is no need for immediate or urgent action to reduce phosphorous use on farms.<br />

14. Unlike some other lakes in farming catchments in New Zealand, pressures are not at<br />

critical levels and there is time to work through the problem and respond in a measured<br />

manner to any further changes.<br />

15. We differ on the views of the 42A report, which at Decision Requested: 9.4 states that<br />

water quality is still declining. The SOE report does not report continuing decline in all<br />

measures of water quality, including dissolved reactive phosphorous, which is the form<br />

available for algal growth and is intended to be controlled (directly or indirectly) in many<br />

3


of the proposed rules in section 9 of the proposed plan. Again the SOE report is<br />

helpful 1 :<br />

16. Finally we would like to add that the Council have not determined the relationship<br />

between land practices and critical waterbody phosphorus concentrations at which<br />

significant adverse effects occur, as noted in the submission of Fert Research<br />

discussed at Decision Requested 9.19. There are a range of phenomena, not related to<br />

agricultural activities, that might contribute to the changing state of <strong>Brunner</strong>, including<br />

discharges associated with land slips and erosion, and septic tank discharges from<br />

settlements on the shores of the lake.<br />

17. To conclude this section, <strong>Federated</strong> <strong>Farmers</strong> do not accept that stringent controls on<br />

phosphorous use are necessary, particularly in light of farmer acceptance of good<br />

management practices to achieve improved management of nutrients and better farm<br />

efficiency. Levels of dissolved reactive phosphorous (phosphorous that is available for<br />

utilisation by algae) are stabilised or in decline, and there is no proven link between<br />

land use practices and the supposedly declining state of the lake.<br />

2. The economic and social implications for Lake <strong>Brunner</strong> farmers and the wider<br />

region.<br />

18. In our submission at section 6.6, <strong>Federated</strong> <strong>Farmers</strong> requested that Council fully<br />

consider the financial implications to farming businesses in the Lake <strong>Brunner</strong><br />

Catchment, as required by the RMA, under the proposed Lake <strong>Brunner</strong> Special Area<br />

provisions. At Decision Requested: 9.5 the 42A report recommended accepting this<br />

1 West Coast State of Environment Report 2011. Page 41. ‘Lake <strong>Brunner</strong> DRP 1992 <strong>–</strong> 2011<br />

4


submission, with the comment that Council is sensitive to the fact that some of the<br />

provisions within the Plan will result in financial implications on Lake <strong>Brunner</strong><br />

landowners.<br />

19. At Decision Requested: 9.6 the 42A report recommends the Council accept in part our<br />

submission and insert a non-notification clause in Rules 83 and 84, which will make the<br />

plan more efficient to administer. This is appreciated, but <strong>Federated</strong> <strong>Farmers</strong> also ask<br />

that the Council consider not applying resource consents fees on consents required<br />

under new provisions for the initial three years of the plans life, in recognition of the<br />

benefits to the wider community and the costs to the individual farmers. This is a fair<br />

point in light of the lack of evidence of a causal link between agricultural activities and<br />

changes to the state of the Lake as described in part 1.<br />

20. <strong>Federated</strong> <strong>Farmers</strong> has included some comments on economic and social effects to<br />

assist Council decisions. The information that follows is relevant to all decisions that<br />

potentially affect land value and ability to farm profitably, particularly within more<br />

sensitive areas such as the <strong>Brunner</strong> Catchment as acknowledged at Decision<br />

Requested: 9.18.<br />

21. Our submission notes that restrictive plan provisions can undermine farm values, and<br />

stifle economic activity. Economic effects on the wider community and implications for<br />

the ‘ethic of stewardship’ are also relevant. These concerns link to the purpose of the<br />

RMA described in section 5, and the ‘efficiency and effectiveness’ tests specified in<br />

section 32.<br />

Implications for farm value<br />

22. We have invited Dave Becker, a local real estate agent experienced in rural sales, to<br />

comment on the relationship between saleability or value of properties and the<br />

developing response of the Council to water quality in Lake <strong>Brunner</strong>. We think Dave<br />

has insights that will be helpful to the Council and will ask him to talk about this aspect<br />

of our evidence at the hearing.<br />

Economic and social implications for the wider community<br />

23. In addition to adverse effects on individual farm businesses, limiting farm production,<br />

either directly through nutrient limits, or indirectly through the creation of uncertainty or<br />

disincentives to investment, will reduce economic and social benefits to the community<br />

that would otherwise result.<br />

24. For example the model Southland dairy model farm, a 579 cow farm, showed farm<br />

working expenses for the 2010/2011 year of $746,935, or $1290 per cow. 2 Most of<br />

2 There is no model available for the West Coast, but we think these figures are representative. Model farms are<br />

compiled from figures averaged across a number of ‘monitor farms’ in the region. The source for these figures is<br />

Farm Monitoring Report 2011 <strong>–</strong> Pastoral Monitoring: Southland Dairy. [Online] http://www.mpi.govt.nz/newsresources/publications?title=farm%20monitoring%20report<br />

5


these expenses are sourced locally and relate to labour, contractor and professional<br />

fees, bought in feed, and other local services. Using the Southland model as a guide,<br />

we estimate that the increase of 5250 cows milked on the West Coast reported in the<br />

2011/2012 year, represents an additional $6,777,500 in farm working expenses, the<br />

majority of which directly enters the local economy. Added to the benefits generated<br />

on-farm, almost all milk produced on West Coast Farms is processed locally at<br />

Westland Milk products, a major employer in the region. In other words, reducing<br />

opportunities for farm production, has a directly proportional effect on jobs and<br />

opportunities for enterprising West Coasters.<br />

Relationship between impacts on farm values and stewardship<br />

25. Methods that undermine farm value, will also undermine the sense of ownership of<br />

farms and environmental issues related to them. This is important because voluntary<br />

methods and facilitating behavioral change have already proven very valuable in<br />

managing nutrient inputs to <strong>Brunner</strong> and are an aspect of the ethic of stewardship,<br />

which the Council is required to ‘have particular regard to’ under section 7 (aa) of the<br />

RMA. We think that the following from the section 32 report for the proposed Land and<br />

Water Plan, produced at the time of notification fairly reflects the value of voluntary<br />

action in improving farm practice in the Lake <strong>Brunner</strong> catchment:<br />

Farm plans had been developed with farmers in the catchment in 2005. These<br />

were a non-regulatory approach to improving systems of which some farmers had<br />

implemented the recommended best practice. Good work was undertaken by<br />

landowners through the installation of fencing and bridging, but unfortunately not<br />

everyone participated in this project. With new landowners in the catchment and<br />

changes in policy proposed, a review of these plans would provide new<br />

opportunities for reducing adverse effects on the environment through current<br />

farming practice.<br />

This method is seen as a positive approach towards identifying and working with<br />

landowners to come up with solutions and timeframes for putting in place best<br />

practice systems which not only benefits the landowners, but also has a positive<br />

environmental benefit. It is also another opportunity for farmers to demonstrate the<br />

value of non-regulatory tools in achieving positive change.<br />

26. Contrary to the submission of Fish and Game discussed at Decision Requested: 9.54,<br />

we see farm plans and education as effective in achieving improvements. Widespread<br />

support for improved effluent management, stock exclusion and stock crossings to<br />

reduce P loss are evidence of the ability of farmers to change once properly equipped<br />

with appropriate information.<br />

6


3. The proposed policy framework for the Lake <strong>Brunner</strong> catchment<br />

3.1 Objective 9.2.1 <strong>–</strong> To improve the water quality of Lake <strong>Brunner</strong> by managing<br />

the adverse effects of activities in the catchment to reach an average water<br />

clarity of 5.3m by 2020, and then maintain or enhance this clarity.<br />

28. In further submissions <strong>Federated</strong> <strong>Farmers</strong> opposed the submission from the<br />

Department of Conservation to replace water clarity with Trophic Lake Index (TLI) as<br />

the key parameter in Objective 9.2.1. The 42A report recommends accepting this<br />

submission at Decision Requested: 9.15.<br />

29. We oppose the use of TLI because it makes the policy framework subject to nitrogen<br />

(in addition to phosphorous, clarity, and algal biomass), which has been barely<br />

addressed at all in the Proposed Regional Land and Water Plan. We therefore fear that<br />

the inclusion of TLI as parameter in Objective 9.2.1 creates a lacuna in the plan, and<br />

thus creates scope for legal challenge that was not previously present.<br />

30. The information we have suggests that Nitrogen:<br />

is not a limiting nutrient in Lake <strong>Brunner</strong>;<br />

is a costly contaminant to regulate or control with any certainty because is readily<br />

soluble in water;<br />

is unlike phosphorous in that nitrogen loss is more difficult to accurately measure<br />

and provide direct regulatory measures to manage;<br />

there is scope to reduce nitrogen loss through good practice methods, but some of<br />

these measures can be incredibly expensive and have not been trialled in high<br />

rainfall environments such as the West Coast;<br />

a large proportion of nitrogen loss is to groundwater, and is difficult to observe or<br />

measure, and regulators are very reliant on predictive models.<br />

31. <strong>Federated</strong> <strong>Farmers</strong> recommends that the Council avoid opening a proverbial ‘can of<br />

worms’ and leave water clarity as the key parameter in Objective 9.2. Not only is water<br />

clarity simpler to deal with, but it also directly represents that values that the plan<br />

change is seeking to protect. As noted in the section 32 report, and repeatedly stated<br />

throughout pre-consultation the key issue for Lake <strong>Brunner</strong> is phosphorous and lake<br />

clarity, and this should remain the focus of the plan change.<br />

32. Failing this, we submit that West Coast Regional Council exercise its right to undertake<br />

further consultation on the use of TLI as the key parameter in Objective 9.2.1. At no<br />

point during the preparation of the plan was TLI discussed as a parameter of interest. It<br />

is only with the release of the 42A report, at this very late stage, that we have become<br />

aware of it.<br />

33. <strong>Federated</strong> <strong>Farmers</strong> notes that the 42A report recommends rejecting submissions<br />

requesting reference to nutrients besides phosphorous (at Decision Requested: 9.17,<br />

Decision Requested: 9.20) Our comments on the use of TLI at paragraphs 28-32 are<br />

also relevant to discussions of other nutrients.<br />

7


3.2 Policy 9.3.3 <strong>–</strong> To reduce the amount of phosphorous discharged in the Lake<br />

<strong>Brunner</strong> catchment.<br />

34. In further submissions, <strong>Federated</strong> <strong>Farmers</strong> supported the proposed change to the<br />

wording of this Policy by Fert Research to refine the focus of Policy 9.3.3 to<br />

phosphorous discharged to water, rather than phosphorous applied to land. It is good<br />

to see the staff report recommend this submission is accepted at Decision Requested:<br />

9.19. We also support the submission of Westland Milk Products as discussed at<br />

Decision Requested: 9.21 for the same reasons.<br />

3.3 Policy 9.3.4 <strong>–</strong> To require discharges of dairy effluent in the Lake <strong>Brunner</strong><br />

catchment to be to land rather than directly to water.<br />

35. In our submission, <strong>Federated</strong> <strong>Farmers</strong> asked that Council: Carefully consider the actual<br />

costs and benefits of the proposed objectives, polices, and rules. The importance of<br />

balancing costs and benefits is acknowledged at Decision Requested: 9.24.<br />

36. For example, effluent application systems are a technically complex area, and a variety<br />

of problems arise if rules and consents conditions are subject to prescriptive, rather<br />

than outcome-based criteria. Discussions with experts 3 suggest that the use of deferred<br />

irrigation of effluent (storage) is not feasible on the humped and hollowed and high<br />

rainfall land in the <strong>Brunner</strong> catchment. The pond calculator model for the West Coast<br />

predicts that optimum soil moisture conditions do not persist for long enough to get<br />

FDE onto land fast enough to keep ponds empty, and that it will be very difficult for<br />

farmers to maintain a useful irrigation buffer, even with very large ponds. Furthermore,<br />

Michael’s experience in Southland is that large storage ponds are prone to failure as<br />

clay liners erode and crack, or as synthetic liners are compromised by rising methane<br />

gas from decomposing soil organic matter. Unsuitable design can also lead to severe<br />

problems with odour. Thus, any storage pond must be suitable for the climatic<br />

conditions and designed and constructed to a very high engineering standard,<br />

otherwise a structure intended to achieve certainty and reduced contaminant loss from<br />

the farm system will have the opposite effect, with wasted capital, on-going worry for<br />

farmers, and lack of certainty for the Council the likely result.<br />

37. With effluent systems, <strong>Federated</strong> <strong>Farmers</strong> prefers simple systems that achieve certainty<br />

of outcome, and that come at reasonable cost so as to leave farmers with resources to<br />

address other areas of environmental performance. Rushing through with prescriptive<br />

solutions, even as researchers are working to develop effluent systems suitable for<br />

high rainfall environments, is likely to lead to high cost and poor environmental<br />

performance in the long term.<br />

3 Dr Dave Houlbrooke pers comm 9-01-2012<br />

8


3.4 Policy 9.3.5 <strong>–</strong> To prevent stock access to waterways<br />

Rule 9 <strong>–</strong> Grazing and livestock access to riparian margins<br />

Rule 10 <strong>–</strong> Grazing and livestock access to riparian margins in the Lake <strong>Brunner</strong><br />

catchment<br />

38. <strong>Federated</strong> <strong>Farmers</strong> supports the exclusion of stock from waterways, and understands<br />

that it should be attempted where practicable. We also think that the plan change as<br />

notified is a reasonable approach, that reflects generally expected behaviour, economic<br />

efficiency, and the stable or improving water quality on the West Coast reported in the<br />

SOE report. Accordingly, we have submitted in support of Policy 9.3.5, Rule 9 and Rule<br />

10 as notified.<br />

39. Although our submission requested an amendment to Rule 10 to include an<br />

explanation that stock exclusion can include exclusion by means of natural terrain of<br />

the banks of a river or creek, we are satisfied with the response of the 42A report, at<br />

Decision Requested 18.1.57, that this is already provided for by clause (a) of Rule 10<br />

‘all farmed stock animals shall be prevented from entering any waterway…’<br />

Further submissions<br />

40. A number of submissions were received requesting that policies and rules relating to<br />

stock access to water and placement of riparian fencing be strengthened and/or<br />

extended to other parts of the region besides Lake <strong>Brunner</strong>. <strong>Federated</strong> <strong>Farmers</strong> lodged<br />

further submissions on all of these. A summary follows:<br />

Submitter Within <strong>Brunner</strong> Catchment Remainder of Region<br />

Plan change as notified Policy 9.3.5 <strong>–</strong> prevent stock access<br />

West Coast Tai Poutini<br />

Conservation Board<br />

Rule 10 - 1 m setback from water<br />

Minimum 5 m setback, native vegetation<br />

required - Decision Requested: 18.1.54<br />

Paul Sutton Amend Rule 10 <strong>–</strong> …any fences to be placed a<br />

minimum of 1 10 metres from the edge of the<br />

waterway. - Decision Requested: 18.1.53 and<br />

Decision Requested: 18.1.63<br />

Fish and Game Amend Rule 10 <strong>–</strong> …any fences to be placed a<br />

minimum of 1 3 metres from the edge of the<br />

waterway. - Decision Requested: 18.1.58<br />

Forest and Bird Amend Rule 10(a) to provide for fences to be<br />

set back from the waters edge to ensure the<br />

distance will prevent surface run off. Decision<br />

Requested: 18.1.62<br />

9<br />

Rule 9 <strong>–</strong> The activity does not cause or<br />

induce conspicuous slumping, pugging, or<br />

erosion.<br />

5 m setback, native vegetation required<br />

New Rule 7(f) <strong>–</strong> Riparian margin of minimum<br />

10 metres which is fenced off to prevent<br />

access by stock - Decision Requested:<br />

18.1.43<br />

Extend amended Rule 10 to entire region -<br />

Decision Requested: 18.1.53<br />

Implement Policy 9.3.5 region-wide -<br />

Decision Requested: 9.32


Department of Conservation Change fencing distance from the waterway<br />

from 1 metre to 3 metres.<br />

Decision Requested: 18.1.56<br />

10<br />

Implement Policy 9.3.5 region-wide -<br />

Decision Requested: 9.29<br />

41. We see the relief sought by the above submitters as unnecessary and unreasonable in<br />

consideration of the overall broad judgement of likely environmental benefits against<br />

economic and social cost to farmers and the wider community. We therefore support<br />

the recommendations in the 42A report to reject these submissions.<br />

42. In regard to requests to extend the 1 metre buffer within the Lake <strong>Brunner</strong> catchment<br />

up to 10 metres, or to extend stock access provisions for Lake <strong>Brunner</strong> to the<br />

remainder of the region, we note that:<br />

Very substantial areas of land will be lost to production, for little environmental<br />

improvement in terms of the actual state or health of the receiving water body.<br />

Due to the potential loss of land and social and economic effects that might arise<br />

if the Council were to accept further submissions, we question the<br />

recommendation in the 42A report at Decision Requested: 9.30 to reject our<br />

submission on possible costs of Policy 9.3.5;<br />

outside the <strong>Brunner</strong> catchment, water quality is good or getting better in all<br />

surface water bodies, which suggests that increased regulatory intervention is not<br />

necessary;<br />

compared to other parts of New Zealand, West Coast farms are relatively smaller<br />

and with lower stocking rates;<br />

stock exclusion can be very difficult to achieve on dry stock properties where a<br />

permanent 7 wire fence is required to stop stock, land may be steep with<br />

numerous intersecting streams and ephemeral watercourses, and where farmers<br />

often rely on natural flowing water for stockwater. Dry stock properties are also<br />

generally farmed less intensively than dairy farms, with lower densities of animals<br />

that can impact on creeks;<br />

pest plants are a major problem on ungrazed land on the West Coast, and this<br />

will be no different in riparian areas. Controlling these, or managing an effective<br />

transition to native vegetation often results in much higher costs than building a<br />

permanent fence in the first place;<br />

stock exclusion can result in lack of access to maintain creek beds, which will<br />

result in enhanced flood risks.


3.5 Policy 9.3.6 <strong>–</strong> To reduce the loss of phosphorous to Lake <strong>Brunner</strong> associated<br />

with the intensification of land, by managing phosphate fertiliser use in the<br />

catchment so that no net increases in annual use occurs per property.<br />

43. As notified, Policy 9.3.6 will likely create problems with equity between farmers and<br />

unnecessary complexity as phosphorous fertilizer (P) use on farm land in <strong>Brunner</strong> is be<br />

pegged to past levels (grandparenting). <strong>Federated</strong> <strong>Farmers</strong> are particularly concerned<br />

about the phrase ‘so that no net increases in annual use occurs per property’, at the<br />

end of the Policy.<br />

44. Work undertaken in the Taupo catchment 4 has found that grandparenting results in<br />

farms with historically high nutrient use finding it much cheaper to cap at current levels<br />

than farmers who have not. This study found that reducing nitrogen leaching on the<br />

more intensive farm could cost between $3.41 and $14.70 per kilogram. For the less<br />

intensive farm the cost was between $52 and $84 per kilogram. These figures apply to<br />

caps on nitrogen, but the implications for caps on P use are very similar.<br />

45. Grandparenting has particularly serious implications for farms that have used debt to<br />

grow their business. Farms that are able to demonstrate a historic pattern of relatively<br />

high P-use will be able to provide certainty to lenders that they can continue to farm<br />

profitably, while farms that have used relatively low levels of P (and low environmental<br />

impact) will not and will suffer substantially both in terms of reduced bankable value<br />

(but not debt) and reduced access to credit.<br />

46. With grandparenting, development may still be possible, but will be very costly, because<br />

extensive investigative work, farm plan preparation, and monitoring will be required to<br />

demonstrate a net increase in phosphorous-loss, and there is no evidence that this will<br />

make any difference to the lake or is even necessary from an environmental point of<br />

view.<br />

48. Policy 9.3.6 is also inconsistent with subsequent methods which confine limitations on<br />

phosphorous use to land developed since 1st January 2011. This is confusing because<br />

the intent of the council (the policy) is not consistent with specified actions (i.e. rules).<br />

49. In further submissions we support the submission of Fert Research on Policy 9.3.6,<br />

which is discussed at Decision Requested: 9.36 of the 42A report. We see the change<br />

recommended by staff as an improvement to Policy 9.3.6 that increases clarity and<br />

focuses the policy on land development, rather than ‘intensification’, which could apply<br />

to virtually any increased use of fertiliser over historic levels.<br />

3.6 Rule 14 <strong>–</strong> Humping and hollowing, flipping, v-blading, or contouring in the<br />

Lake <strong>Brunner</strong> catchment<br />

4 Review of Implications of nutrient caps on New Zealand’s agriculture. N Hoogaveen. Completed April 2006 [Online]<br />

http://www.fertresearch.org.nz/research/research-results/completed-research<br />

11


50. In our submission, <strong>Federated</strong> <strong>Farmers</strong> sought the inclusion of an explanation to Rule<br />

14 to the effect that: This rule is not intended to prohibit further development, but<br />

requires the applicant to consider methods of reducing potential future phosphorus loss<br />

into Lake <strong>Brunner</strong>. The 42A report recommended the Council accept this submission<br />

at Decision Requested: 18.1.73. <strong>Federated</strong> <strong>Farmers</strong> appreciates this recommendation.<br />

3.7 Rule 72 <strong>–</strong> Application of fertiliser<br />

51. In submissions, <strong>Federated</strong> <strong>Farmers</strong> opposed in part amendments to Rule 72 to only<br />

provide for application of fertiliser as a permitted activity, as part of land development in<br />

the Lake <strong>Brunner</strong> catchment, if the solubility of the fertiliser is less than 10%. This very<br />

low solubility makes Rule 72 very difficult to apply in the <strong>Brunner</strong> catchment because<br />

10% is too low a solubility to support the rapid plant growth necessary for successful<br />

land development, and to consolidate sediment. This is unnecessary given that land<br />

development in the <strong>Brunner</strong> catchment is a discretionary activity under Rule 14.<br />

52. In our submission we requested that provision for higher solubility fertiliser might make<br />

Rule 72 more useful. The staff recommended the Council reject our relief sought at<br />

Decision Requested: 18.5.9.<br />

53. In further submissions, <strong>Federated</strong> <strong>Farmers</strong> opposed the submission of the Department<br />

of Conservation, discussed at Decision Requested: 18.5.10, because the imposition of<br />

farm plans across the region would be very difficult to enforce, and would be a severe<br />

administrative burden for the Council, and would seek to address something that is a<br />

non-issue according to water quality in the SOE report. The 42A report recommended<br />

the Council reject this submission.<br />

3.8 Rule <strong>–</strong> 83 Application of phosphorous fertiliser associated with Rule 14 in the<br />

Lake <strong>Brunner</strong> catchment<br />

54. In submissions, <strong>Federated</strong> <strong>Farmers</strong> sought that Council either removes condition (ii) of<br />

Rule 83 or clarifies:<br />

how the amount of fertiliser is to be defined;<br />

how properties are to be established where boundaries change or lease<br />

agreements are established;<br />

how an annual average will be established in the absence of accurate records;<br />

and;<br />

how an appropriate bench mark period will be established given concerns with<br />

the 2005 <strong>–</strong> 2010 years<br />

Condition (ii) of Rule 83 is:<br />

The average amount of phosphorous fertiliser applied per property per year is to<br />

be no more than the annual average applied between 2005-2010.<br />

55. No submissions were received in opposition of this submission.<br />

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56. We are relieved to see that the 42A report, Decision Requested: 18.5.60 recommends<br />

that Council accept in part this submission by making clause (ii) a discretionary matter<br />

rather than a determinant of activity status.<br />

57. We provide lengthy comment on Rule 83 in our submission. There is no need to repeat<br />

it here, however the main points are:<br />

<strong>Farmers</strong> use different types and mixes of fertiliser from year to year, which makes<br />

historic amount and solubility of P applied very difficult to establish;<br />

The ‘per property’ proviso in condition (ii) will become very complex to administer<br />

as properties are subdivided, change hands, amalgamate, are leased out and so<br />

on;<br />

Some owners (whether in their own or a previous owners account), will not have<br />

the necessary records to implement Rule 83;<br />

The benchmark years of 2005-2010 were an economically difficult time for many,<br />

with the result that P use was likely to be restricted. This amplifies the inequity with<br />

other land users who have developed land and made capital dressings of P over<br />

the same period.<br />

59. <strong>Federated</strong> <strong>Farmers</strong> also submitted in support of the submission of Fert Research on<br />

Rule 83, discussed at Decision Requested: 18.5.61. We agree with the relief sought<br />

and reasons given in the Fert Research submission and note also the recommendation<br />

of the 42A report to accept in part this submission.<br />

3.9 Schedule Twelve<br />

59. At Decision Requested 12.1, <strong>Federated</strong> <strong>Farmers</strong> requested that Schedule Twelve be<br />

amended in consultation with <strong>Federated</strong> <strong>Farmers</strong> and farmers in the Lake <strong>Brunner</strong><br />

Catchment, and taking into consideration the actual costs and benefits of the schedule.<br />

The 42A report recommended that Council accept in part the submission, but did not<br />

suggest changes, referring instead to the relief sought by Fert Research.<br />

60. In further submissions, <strong>Federated</strong> <strong>Farmers</strong> submitted in support of the submission of<br />

Fert Research on Schedule Twelve which requested a number of changes to enhance<br />

clarity and use-ability. The 42A report recommended that Council accept in part the<br />

submission, and recommended the implementation of all but one change.<br />

61. The 42A did not recommend deletion of the final paragraph as it may send the wrong<br />

message to landowners. In the view of <strong>Federated</strong> <strong>Farmers</strong>, the last paragraph of<br />

Schedule Twelve resembles policy rather than part of a schedule, which is confusing.<br />

We also suspect that the approach of rigidly adhering to Olson P of 30 is not technically<br />

correct (as optimum P varies significantly with soil properties), and await with interest<br />

the comment of Fert Research in this regard. In support of the submission of Fert<br />

Research, we request that this part is either removed, or else re-phrased as a<br />

suggestion rather than an imperative.<br />

3.10 Policy 9.3.7 <strong>–</strong> To encourage methods of wintering stock that will reduce the risk<br />

of phosphorous loss in the Lake <strong>Brunner</strong> catchment, including the<br />

management of effluent that results from wintering methods.<br />

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62. In our submission on Policy 9.3.7, discussed at Decision Requested: 9.38, <strong>Federated</strong><br />

<strong>Farmers</strong> requested an amendment to the explanation to make it clear that the policy is<br />

non-compulsory in nature. The 42A report recommended Council reject this<br />

submission. We maintain that conventional wintering in the catchment may be the only<br />

practicable option for many, for example if market conditions result in shortage of land<br />

for winter grazing elsewhere, or biosecurity issues, (such as Tb) restrict stock<br />

movements.<br />

63. In further submissions, <strong>Federated</strong> <strong>Farmers</strong> responded the submission of the<br />

Department of Conservation (at Decision Requested: 9.37), who sought Rules to<br />

manage winter grazing. <strong>Federated</strong> <strong>Farmers</strong> members fear that ‘rules’ for winter grazing<br />

will result in excessive cost in light of the nature of the problem and concessions<br />

already made by farmers in the <strong>Brunner</strong> catchment. An obvious fear is that rules will<br />

involve requirements for ‘alternative’ wintering practices, such as wintering barns, to<br />

demonstrate reduced phosphorous loss. <strong>Federated</strong> <strong>Farmers</strong> seeks to avoid this<br />

outcome because wintering barns are very costly, and introduce technical complexity<br />

around animal welfare and diet which must be carefully managed. Furthermore,<br />

wintering barns encourage high intensity farming as farmers attempt to recover the<br />

cost, and take advantage of the ability of wintering barns to achieve efficient feed<br />

utilisation, and increase cow numbers on the milking platform. With future policy<br />

responses to stock wintering, the Council is better to avoid prescriptive policy<br />

responses, and focus on good wintering practice, and to ensure that solutions are cost<br />

effective and achieve good environmental outcomes.<br />

4. Other Matters<br />

4.1 Policy 4.3.6 <strong>–</strong> Council will require the use of bridges, culverts, and other<br />

methods where a farmers causes a herd of cattle to cross any river or<br />

permanently flowing creek, at any farm raceway, more than ten times in any<br />

month for herds larger than 500 cattle, or more than 20 times in any month for<br />

herds less than 500 cattle. A crossing is one-way only.<br />

This Policy also applies for dry stock where more than 50 animals cross any<br />

river or permanently flowing creek more than 20 times per month.<br />

63. <strong>Federated</strong> <strong>Farmers</strong> are pleased to see the recommendation to accept our submission<br />

and amend Policy 4.3.6 at Decision Requested: 4.17 of the 42A report. The suggested<br />

changes make sense and make the plan more coherent and easier to understand, and<br />

are fairer because cattle are treated equally with other stock types.<br />

64. <strong>Federated</strong> <strong>Farmers</strong> made further submissions on the submission from Fish and Game<br />

discussed at Decision Requested 4.18. This submission includes a request to extend<br />

controls on stock crossings to any situation where a farmer causes cattle to cross a<br />

‘river or permanently flowing creek’. In response to the submission of Fish and Game, it<br />

is not reasonable or efficient to require that every place where animals might<br />

conceivably cross a stream has a fence or a culvert. We support the 42A report which<br />

recommends the Council reject this submission.<br />

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65. The phrase ‘licence to contaminate’, as used in the submission from Fish and Game is<br />

confusing and unhelpful because it is not actually the Policy but the methods that<br />

implement it that regulate the activity in question. It is also an unnecessarily emotive<br />

way to describe what is legally allowed to occur under section 15 of the RMA. Policy<br />

4.3.6 does not act as a ‘licence to contaminate’, but merely specifies the line between<br />

what is generally allowed as a permitted activity, and activities that requires a resource<br />

consent.<br />

4.2 Rule 17 <strong>–</strong> Stock crossings in the Lake <strong>Brunner</strong> catchment<br />

66. <strong>Federated</strong> <strong>Farmers</strong> submitted that the Council defer the adoption of Rule 17 until 1 July<br />

2012. The 42A report at Decision Requested: 18.1.81, recommended rejecting this<br />

submission because water quality continues to decline within the catchment, and<br />

therefore stringent measures are necessary. We do not agree with this view, however<br />

the question is academic because the plan will not be operative until after the date<br />

specified.<br />

4.3 Outstanding Natural Landscapes<br />

67. The submission of the West Coast Tai Poutini Conservation Board includes relief<br />

sought to recognise and provide for Outstanding Natural Features and Landscapes,<br />

and include a new Objective and new Policy.<br />

68. <strong>Federated</strong> <strong>Farmers</strong> sees that a regional plan is not the appropriate place to discuss this<br />

as the relief sought is likely to cause conflict and confusion over Council roles. ONFLs<br />

should only be dealt with at the RPS or District Plan level. For the above reasons<br />

<strong>Federated</strong> <strong>Farmers</strong> endorses the recommendation of the 42A report at Decision<br />

Requested: GS 21, Decision Requested: 3.4 and Decision Requested: 3.11, to reject<br />

the submission because it is outside of the scope of the proposed plan.<br />

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