3.2.5 Comparison with other deer systems

The MAF base model used in this exercise to examine the financial implications of accommodating the constraints to organic production identified by the workshop members is based on an intensive Southland/South Otago deer unit. On more extensive deer units, such as in the hills of Canterbury, Otago and Southland, minimal change might be required to qualify as organic. These farms would be characterised as units with low stocking rates (<5 su/ha), minimal chemical inputs, little handling of deer and few weed problems. A small premium would be required and therefore funding during the conversion period would not be a major constraint to producers exploring the organic option.

3.2.6 Risks and the impact of risk on financial performance

The demand and consequently the likely premiums for venison and other products from the deer industry are not well understood. A commentary from the marketing company represented at the workshop suggested that the premium for organic venison would not be as high as other organic products because the market already has a perception that venison is a natural product. More research and marketing is required to develop a sustainable premium for organic venison. Uncertainty over the size of the market and the margins paid over and above conventional product is therefore one of the major constraints to deer farmers converting to organic supply. The difficulty of funding the conversion is another.

In the MAF base model used in the current study, a drop in premium would have an immediate effect on the financial viability of the enterprise. On the more extensive deer units in the hills of Canterbury, Otago and Southland, minimal change might be required to qualify as organic and, as such, little premium would be required and therefore additional funding during the conversion period would not be a major constraint to extensive producers exploring the organic option.

A severe outbreak of lungworm is a major threat to the venison operation. This would impact heavily on the proportion of stock that could be finished to specification. If registered to CERTENZ rather than BIO-GRO (as the CERTENZ standards allow some intervention without the loss of certification), there is greater certainty in being able to supply to specification and hence less risk to profits.

Removal of fertiliser nitrogen means that a more conservative approach must be taken for feed budgeting. In dry environments and high pH soils, the inability to maintain soil fertility and legume growth is compromised by the limited range of fertilisers available.

In the long-term the greatest risk to the deer sector, and all sectors, is weed infestation as it affects all aspects of land use.

Organic producers would need to be forward looking, good planners and managers, and have different thought patterns to conventional producers. They would need to be proactive and preventative in their management. One of the risks of organic production is that if something unforeseen occurs there is a limited range of allowable responses to fix a problem if the organic status of the animals and their products is to be maintained.

Organic producers do not have the same knowledge and management infrastructure available to them as conventional producers. Gaining knowledge can therefore be more difficult, more time consuming and more expensive.

3.3 Arable

3.3.1 Prioritisation of issues

The complexity of the issues involved in developing a sustainable arable system was highlighted at the workshop.

Weed control ranked as one of the most important issues facing arable farmers, and cultivation is one of the main control options available to organic arable farmers. However, repeated cultivation passes places additional pressure on the physical properties of the soil and could result in greater organic matter content and nitrogen losses from the root zone. Increased fossil fuel use is another consequence of the reliance on mechanical cultivation. Weed problems can to some degree be countered by crops that don’t allow weeds to seed (e.g., process crops), but this compromises flexibility. In comparison, Brassica seed crops are best avoided because of complications later with volunteers/seed dispersal.

Livestock offer a biological weed control option. Stock performance may have to be compromised, however, to ensure effective clean up of weeds or crop residues to prevent carry over effects. Other weed control options, such as the use of compost or green manure, would supply nitrogen and reduce the number of cultivations, but may enhance the likelihood of disease. The lack of nitrogen fertiliser options was identified as a constraint that limited both the range of crops that can be grown and their yield.

The requirement for crop rotations to manage nutrients, pests and weeds, and soil physical properties was seen as reducing the flexibility in the cropping options that can be run in any one year in the organic system. Birds were seen as a bigger problem in organic systems.

With livestock representing a bigger part of the business because of the need for a pasture phase for building organic matter and nitrogen fertility, the animal husbandry skills of the organic operator are of greater importance than in a non-organic arable system.

The need for the organic arable farmers to learn new skills and be proactive in their management style to prevent rather than cure a problem was also emphasised by the group. The workshop agreed that organic arable systems require very good management skills to make them work.

Infrastructure and industry related constraints were divided between three moderately important issues. As at the sheep and beef workshop, the certainty of returns in the long-term was an important issue, along with concerns about the size of the organic market. The workshop identified the risk of price variation in the small domestic market for organic grains, but also identified potential export opportunities for grass and clover seeds into European markets.

The dependency on fewer crop options and the exposure of the organic producer to one or two major processors (e.g. process peas) adds further uncertainty. The group identified maintaining flexibility and the cash flow of the farm business as important considerations for arable farmers in general. There was a need for both certifying authorities to further develop market recognition of their standards.

Finally, the negative view of some conventional growers was seen as a "them versus us" factor that was discouraging growers from entering the organic market. The workshop participants felt that in reality, this attitude was directed at the more "politically motivated" part of the organic movement rather than the commercial organic growers themselves. There was a genuine respect among the workshop participants for each other’s choice of production system. Participants recognised that there is a need to develop an attitude of co-operation and communication between organic and non-organic growers, as the sharing of knowledge, both ways, is vital for the continued development of the whole arable industry.

In summary, methods of weed control emerged as a big issue in the organic system, as did maintaining fertility. The knowledge and skills of the grower was the other main technical issue, with knowledge required in the areas of how to develop a sustainable system, soil nitrogen supply, methods of weed control, and management techniques to prevent problems. Heightened skills in animal husbandry were seen as another issue facing the organic arable producer. The industry and infrastructure issues pointed to a need for strong leadership to emerge to secure reliable markets for organic produce, promote the organic standards to the arable markets, and encourage good communication and relationships between conventional and organic producers. The maintenance of flexibility in the production and business system was important.

Alternative land uses are resulting in falling areas of arable crops in Canterbury over the last few seasons, and this is not encouraging conversion to organic supply. Few arable operators are known to be considering conversion to organics.

Technical constraints to conversion to organic arable production identified by the Focus Group are listed in Table 12. Infrastructure and industry constraints are shown in Table 13.

Table 12 Technical constraints identified by the Focus Group, and their relative importance in conversion to organic arable production.

Issue Comment Rating1
Long-term soil fertility/biology of soils Nutrient (nitrogen) management, biological activity of soil Many
Physical health of soil Additional cultivation for weed control causing soil structural decline, loss of carbon and nitrogen

Crop rotation with organic matter soil structure in mind

Many
Animal health See sheep and beef section
Pests Managing outbreaks. Techniques to identify and monitor pest and weeds

Management of pests and weeds

Few
Disease Disease control Few
Weeds Shift from high to low fertility weeds

Need effective weed control and management strategies particularly for Californian thistle

Producing seed to purity standard

All
Genetics/adaptation Breeding for resistance Few
Animal nutrition/ feed/ stock Pasture composition, mineral content, and nutritive value
Animal management Integrated use of crops Many
Pasture/crop seed Limited availability of organic seed Few
Energy use Higher energy use Many
Skills and knowledge of manager New skills and proactive management. Must have a very good adviser to provide the many answers needed

Need information on how to grow specialist seed crops

Surviving the transition

All

1 The words "All", "Many" and "Few" rank the importance of an issue in terms of the proportion of votes it received by the workshop members.

Table 13 Infrastructure and industry - Constraints identified by the Focus Group, and their relative importance in conversion to organic arable production

Issue Comment Rating1
Signals on premiums/market stability Long-term market size and returns. Market certainty, will the premium or market disappear by the time a grower is certified and producing?

Productivity/premium ratios/trade offs

Impact of other government policies

Many
Standards Standards recognised by the market, ensuring organic food is safe, product quality and point of sale; standards are based on consumer demand

Setting of standards by foreign countries, outside the influence of New Zealand producers and consumers

Problem – two different "types" of certification – CERTENZ, BIO-GRO, compliance costs

Many
Industry infrastructure and strategy Processing capability, open access to markets, capturing more of the downstream value Few
Services Availability of services and skills, information on how to market products profitably Many
Perceptions on organics Polarisation of views "them versus us" Many

1 The words "All", "Many" and "Few" rank the importance of an issue in terms of the proportion of votes it received by the workshop members.

3.3.2 Canterbury arable farming model

The model is based on the Canterbury arable cropping model (MAF, 2000). More than 50 percent of the farm income is generated from growing crops. The whole farm can be irrigated, although in practice there is some dryland pasture where irrigation capacity is insufficient at peak demand. The farm is a mixture of cropping and livestock enterprises (Table 14 and 16). The model farm’s stock policies involve trading lambs and running a 2-year ewe flock for lamb production. Half the ewe flock is replaced each year. There are 110 cows grazed for 12 weeks at $14/cow/week. The Canterbury arable model was used as the base on which to examine the financial implication of addressing the major constraints to organic cropping and livestock production.

In the construction of the organic Canterbury arable cropping system, a number of changes and assumptions were made to accommodate the constraints identified by the Focus Group. These cover area of crop grown (Table 14), organic crop premiums (Table 15), and livestock policy (Table 16).

Table 14 Area of crop grown (ha)

Crops

MAF base model

Organic model

Milling wheat 25 40
Feed wheat 40
Malting barley 15 8
Grass seed 40
Clover seed 20
Other small seeds 12 13 (linseed)
Vegetable/brassica seeds 11
Pulses 20 5
Silage (as cash crop) 3
Process Peas 9 55
Irrigated pasture 42 103
Non-irrigated pasture 20 20
Green feed oats 100 or 501
Green manure (ploughed in) 34 or 841
Total 257 257

1 A small area would effectively be in fallow each year.

In addition to changes in crops grown, the following changes were made to the organic Canterbury arable cropping model:

  • reduction in the area under cropping;
  • no fertiliser nitrogen in the organic system;
  • number of cultivations increased for weed control (Higher fuel, vehicle and labour costs per hectare, offset the savings on chemicals use);
  • RPR applied at 450 kg/ha across the whole farm;
  • lower crop yields;
  • weed and pest control costs reduced.

Table 15 Prices for conventional and organic crops

Crop

Conventional

Organic

Yield (t/ha)

Price ($/t)

Yield (t/ha)

Price ($/t)

Milling wheat

6.0

275

4.0

500 (181%)

Barley

6.7

200

4.5

350 (175%)

Linseed

500

1.5

1000 (200%)

Lentils

600

1.0

2000 (333%)

Peas

6.6

300

4.0

500 (167%)

Note: these premiums are based on returns organic arable producers are currently being paid. Values in bracket are the premiums as a percentage of the current conventional price.

Table 16 Summary of the livestock policy on the MAF base and organic arable systems

MAF base model
Opening Buy Natural increase Sell Deaths Close
Ewe lambs 390 390
Ewe hoggets
MA ewes 600 310 300 10 600
Wether lambs 830 0 120 10 700
Wether hoggets 700 690 10
Ram lambs 390 390
MA rams 5 1 1 5
Steer calves
R1yr steers
Cattle grazing 110 cows are grazed for 12 weeks
Organic model
Opening Buy Natural Increase Sell Deaths Close
Ewe lambs 690 320 9 361
Ewe hoggets 361 20 11 330
MA ewes 1200 280 50 870
Wether lambs 0 0 0
Wether hoggets
Ram lambs 690 681 9
MA rams 12 3 3 12
Steer calves 50 0 50
R1yr steers 50 48 2
Cattle grazing 100 cows are grazed for 12 weeks

MAF base model

  • The MAF model farm runs 600 MA ewes, which have 130 percent lambing. All lambs are finished prime.
  • Three hundred ewes are sold and an additional 310 ewes purchased each year.
  • Wether lambs (830) are purchased each year and, of these, 120 are sold before mid winter, with the balance sold in July-September.

Organic model

Stock management

  • Changes made to the organic system are required because of the difficulty of buying organically raised lambs. As a result, the organic system rears its own replacements.
  • The organic farm runs 1,200 MA ewes, which start lambing on 10 August with 115 percent lambing percentage.
  • No routine vaccination, drenching or dipping is done.
  • All wether lambs (681) and 320 ewe lambs are sold prime, 70 percent by 1 December, with the balance sold by May. The remaining 361 ewe lambs are kept as replacements.
  • The organic farm purchases 50 steer calves, which are sold at 20 months.
  • Stock prices are based on modelled performance and the same $/kg carcass weight as for the sheep and beef model.

Agronomic management

  • 1705 bales of hay are made, with 1286 being fed, and 358 t of silage is made of which 222 t is fed in the organic system. Most farmers considered that having a large buffer of supplementary feed was a prerequisite for an organic system. Thus only what is fed is costed in the budget, plus one-fifth of the remainder, as the remainder represents an adverse season buffer. One adverse year in five is assumed.
  • Two different scenarios are modelled for the green manure:
  • 100 ha of green feed oats is grown and grazed, and 34 ha of green manure is grown and ploughed in.
  • 50 ha of green feed oats is grown and grazed, and 84 ha of green manure is grown and ploughed in.

Table 17 Assumptions for conversion to organic production

Farm working expenses MAF base ($) Organic ($)
Permanent and casual wages There is less cropping area on the organic farm, but it is more labour intensive. 21,810 21,810
Agricultural contracting 6,520 6,520
Animal health Fewer animal health remedies are used on the organic system 3,400 1,700
Breeding 190 190
Irrigation (electricity) Extra pasture irrigated. 11,170 12,930
Feed (hay and silage) More supplements are made on the organic system 1,510 6,540
Feed 600 300
Fertiliser No nitrogen fertiliser is used in the organic system 39,180 23,380
Lime Less lime is needed as RPR has a slight liming effect and is more effective on acidic soils 1320 660
Freight Fewer crops are grown in the organic system, with a slightly lower yield 7,920 6,520
Seed dressing Seed dressing is not required in the organic system because no small seeds are grown. 15,470 0
Seeds Pea seed is very expensive, and more peas are grown in the organic system 14,900 19,303
Shearing costs There are more sheep on the organic system 3,142 4,640
Weed and pest control Agrochemicals are not used in the organic system, but inter-row cultivation is needed 44,660 9,950
Fuel More cultivation for weed control 12,640 14,572
Vehicle costs (excl. fuel) More cultivation for weed control 12,780 14,635
Other expenditure Includes, repairs and maintenance, rates, water, communication, insurance, accountancy, administration, and others 42,970 42,970
Cash farm expenditure 240,182 186,620

3.3.3 Financial outcomes from the model

Table 18 shows the financial outcomes for:

  • MAF base model.
  • Organic policy with no premium: changes made to the MAF base model to accommodate constraints to organic production. No premium.
  • Organic with premiums: premiums are based on those currently being received for organic crops (crop premiums for the organic system of 167-333 percent), and the livestock premiums used in the sheep and beef model (i.e. 50 percent for lamb and beef), with 80 percent of both lamb and beef finished to specification.
  • Organic "break-even" 46 percent premium: indicates that an average 46 percent premium is needed on all produce to generate a comparable cash farm surplus to the MAF base model.

Table 18 Key financial indicators of the MAF base and organic models

MAF base model Organic policy
(no premium)
Organic
(with premiums)
Break-even
(46 % premium)
Revenue ($)
Cereals 127,350 65,500 118,600 95,630
Small Seeds 163,400 9,750 19,500 14,235
Other crops 24,900 3,000 10,000 4,380
Process/fresh vegetables 17,820 66,000 110,000 96,360
Total crop revenue ($) 333,470 144,250 258,100 210,605
Sheep income 115,320 85,784 111,690 125,245
Grazing income 18,400 16,800 16,800 24,528
Other farm income 11,100 20,057 32,382 24,177
Less:

Sheep purchases

40,770 1,050 1,050 1,050
Gross farm revenue ($) 437,520 265,841 417,922 383,505
Cash farm expenditure ($) 240,180 186,625 188,010 187,620
Cash farm surplus ($) 146,780 28,662 179,352 145,326

The major effect on the profitability of converting to an organic farming system arises from changes to both the cropping and livestock policies. The change in cropping policy and stock policy, assuming static prices, results in a reduction of $171,679 in gross farm revenue and $118,118 in the cash farm surplus. This decline is driven by the shift to less profitable and productive cropping options, a contraction in the area under cultivation, and a less profitable livestock policy.

Using the premiums currently on offer, cash farm surplus is higher in the model example than in the base model. However, the group considered there were also greater risks associated with this scenario through the loss of flexibility and increased dependency on a few crops, particularly cereals and process peas.

It is reasonable to suggest that funding the reduction in farm income resulting from the changes required in the cropping and livestock policy to accommodate the constraints to organic production during the conversion period would be a major constraint to growing this sector of the primary industry.

If conversion is restricted to the cropping component of the operation and the livestock policy in the MAF base model is retained but run as a non-certified stock enterprise, and the income then adjusted upwards to incorporate the greater area in pasture, the cash farm surplus increases to $122,000. This situation would be permitted as an interim activity. In the long-term, however, the livestock policy would have to shift to organic certification.

Differences between CERTENZ and BIO-GRO

There is little difference between CERTENZ and BIO-GRO in the stringency of their specifications for arable crops. It was therefore concluded at the workshop that the choice of most arable farmers would be to certify under BIO-GRO, because BIO-GRO has been in the organic industry for a longer period of time and therefore is better known and often commands a higher premium than CERTENZ.

However, there is a difference between CERTENZ and BIO-GRO in production specifications when it comes to livestock. It is possible to finish a higher proportion of stock to specification under CERTENZ than BIO-GRO, as the CERTENZ standards allow a greater degree of intervention without the loss of certification. Arable farmers with a large proportion of their earnings coming from sheep and beef may therefore choose to register with CERTENZ if it appears that CERTENZ premiums for livestock remain competitive with BIO-GRO. In practice, the authors understand that some organic arable farms have dual certification.

Accounting for the cost of growing extra green manure

To address the issue of increased cultivation to control weeds in the organic system, a proportion of the green manure crops were ploughed in to assist with the regeneration of the soil structure. Composting as a means of building soil fertility and improving soil structure is at the heart of an organic system. Two scenarios were examined:

Scenario 1: 100 cows are grazed on 100 ha of oats, returning $16,800. This is the scenario shown in Table 18.

Scenario 2: Only 50 ha of oats are grown, and 50 additional ha of green manure are ploughed in. Given the timing and size of feed flows, this action results in a reduction of 50 cows grazed, and income is reduced to $8,400. The alternative is to feed additional supplements at an extra cost of $1,765 and retain grazing of 100 cows. Another option would be an overall increase in premiums of 4.5 percent to account for the cost of ploughing in an extra 50 ha of green manure.

3.3.4 Comparison with other arable systems

The MAF base model used in this exercise to examine the financial implications of meeting the constraints to organic production identified by the workshop members is based on a Canterbury arable cropping unit. The arable sector, like the sheep and beef sector, is characterised by a great diversity of cropping and livestock operational mixes. The extent to which funding the conversion period becomes a constraint to an arable producer will depend on the degree to which the existing cropping and livestock policy has to be changed, and the extent to which this impacts on the financial performance of the business.

3.3.5 Risks and the impact of risk on financial performance

The financial viability of the organic arable sector depends on a significant premium for both the cropping and livestock enterprises. This is because of the less profitable cropping and livestock options, an expansion of the area under pasture, and the lower crop yields in the low nitrogen environment in the organic system.

The workshop identified the risk of price variation in the small domestic market for organic grains, but also identified potential export opportunities for grass and clover seeds into European markets. A reduction in the diversity of crops that can be grown exposes the producer to one or two major processors only (e.g. process peas) and increases the risk and reduces the ability to react to opportunities. Other factors include less flexibility in the crop rotation options and the necessity for a pasture ley to build soil fertility and restore physical structure.

For arable producers, the effect of weed invasions can be immediate and devastating on crop yield, quality and value. The necessity to use mechanical control as the major technique for managing weeds in an organic arable system creates a series of additional threats to the system by impacting on the soil resource. Repeated cultivation will reduce the structure, encourage mineralisation of organic matter and reduce the biological activity of a soil. This reduces the resilience of the soil to extreme events, reduces the window of time when soils can be cultivated, increases the number of cultivation passes to prepare the seedbed, and eventually necessitates the incorporation of increasing amounts of organic matter to preserve current production levels. However, this is countered by a less intensive rotation with a longer pasture phase. Lack of access to nitrogen fertiliser reduces not only production opportunities, but also risk management options.

The risks identified and discussed in the sheep and beef section of this report are also relevant to the livestock component of the arable model.

One of the risks of organic production is that if something unforeseen occurs, there is a limited range of allowable responses to fix a problem if the organic status of the animals and their products is to be maintained. Organic producers need to be forward looking, good planners and managers, and have different thought patterns to conventional producers.

Compared with the wider industry, organic producers do not have the same knowledge and management infrastructure available to them. This causes uncertainty and potentially results in delays in actions.

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