Archived at http://orgprints.org/00003116 |
What are the key issues faced by
organic producers?
In: Organic Agriculture -
Sustainability, Markets and Policies.
Proceedings of an OECD
Workshop held in
23-26 September
2002
Eco Landuse Systems Pty Ltd
E-mail: els.wynen[a]elspl.com.au Website www.elspl.com.au
Note: This article was presented at the OECD
workshop in
Abstract
Concerns facing
organic producers can be divided into two main groups, production and marketing.
In the early days of the organic industry, the production problems of farmers
were emphasised, and research topics were often concentrated on soil, pests and
diseases. More recently, as the industry matures and international trade of
organic products has grown, the importance of market-related issues has come to
the fore. On the one hand, the need for harmonisation of standards and
acceptance of equivalence for market development — which would facilitate
international trade — is recognised. On the other hand, a more serious push
towards domestic consumption seems afoot, which would advantage domestic farmers
but disadvantage producers in exporting countries.
The aim
of this paper is to consider developments in the organic market from the
perspective of producers. What are the key issues for producers at present, and
what are they likely to be in the future? What are the expectations of producers
regarding organic agriculture? What are the trade issues arising from domestic
policy measures to develop organic products, including impacts on developing
countries?
Many
organic farmers all over the world face similar technical, economic and social
problems. These are identified in the following section. However, answers to
these questions depend considerably on where the organic farmer is located. The
geographical location of a farmer is important because soil and climate
differences influence input requirements, yields and total farm production
capacity. Different policy approaches are then discussed, looking at the impact
of policies on those producers for whom they are beneficial and those organic
farmers in other countries that feel the consequences of those
policies.
The aim of surviving or thriving
as an organic farmer can be accomplished in many ways. One component of survival
is the financial viability of the farm. Farm returns are influenced by input
use, total production, product prices and market access, that is, production and
marketing issues. A summary of issues is provided here to serve as a background
for the policy issues, discussed in the next section.
Inputs
In essence, organic farmers
manage soil fertility (often called crop nutrition by conventional farmers) and
combat pest problems (including insects, weeds, fungi, nematodes and diseases)
in a different way than conventional farmers. Management methods may include,
for example, changes in inputs (crop varieties and livestock breeds; nutrients;
predators), rotations (more and different crops and livestock), and timing of
activities (planting dates and harvesting dates).
Thus, one area in which organic
farmers encounter problems in the production of crops and livestock is in the
maintenance of soil fertility and avoidance of pest attacks, while minimising
the environmental effects of their actions. The exact nature of the soil, pest
and environmental issues is geographically determined. For example, in a climate
where frequent small amounts of rainfall occur, weeds are more likely to be a
problem, while warm and humid conditions are more conducive to fungi or pest
problems in crops and livestock. Dealing with these may require a change in use
of other inputs, such as labour and capital.
It is therefore not surprising
that because relatively few farmers use organic practices, many of the
complaints by farmers are centred around lack of knowledge about organic
management methods or about inputs (where to purchase and the efficacy of the
available products). In addition, inputs may be more expensive due to extra
transport and handling charges for those inputs not commonly purchased (Wynen 1992).
It is often assumed that more
labour is needed in organic than in conventional agriculture, but this depends
on the industry and country. Higher values for labour on organic arable and
mixed farms are reported in
Studies on differences in capital
values of land used for organic and conventional production are more difficult
to find. As land values are determined by expected returns, there should not be
a large difference between the two types of farms. Organic farms may require
additional capital due to, for example, changes in farm lay-out (fencing),
storage, change in livestock numbers and in machinery. As these investments are
needed when converting to organic farming, it is especially the farmers in
transition who carry this burden.
Another issue, sometimes
discussed by farmers perhaps more in the past than presently, is the moral
support needed to take the step towards organic management while there is social
pressure against adopting the technology (Wynen
1992).
Outputs
Nutritional and pest constraints
under organic management can result in yield decreases as compared with
conventional agriculture. However, this is by no means always the case,
especially not in areas where conventional agriculture is practised relatively
extensively, such as in the
The variability of yield and financial returns
has been a topic of study in developed countries. Little evidence has been found
that the management system is a major factor in the degree of yield and
financial variability, although some studies show less variability under organic
management (Lampkin and Padel (eds)
1994).
The tendency towards
mono-cropping in conventional farming is reversed on an organic farm. That is,
less financially-rewarding production may be included in the rotation. This
affects the total farm production, and has a negative effect on the gross
returns.
Farm
returns
From the producers’ point of
view, net returns to farming are an important, albeit not the sole,
consideration to continue farming. These net returns are made up of gross
returns for the whole farm minus input costs. The gross returns are dependent on
total production (that is, yields of individual enterprises and rotation
practised on the farm), product prices, and farm
subsidies.
Although the level of prices
influence demand for the product, it is the relative prices of conventional and
organic products that are of importance in consumer decisions. This means that
there are two prices that are of importance. One is the retail price of the
organic product, which is only in part (depending on the product) influenced by
the farm-gate price. As long as organic production is small, the off-farm costs
of marketing the product (including cost of transport, insurance and
distribution) will be high relative to those in conventional products. This
extra cost will need to be recouped by the traders, resulting in high retail
prices. However, in markets where traders have monopoly powers, the retail price
can also reflect, at least in part, monopoly rent.
The other important price is the
retail price of conventional products. External costs of conventional farming
practices (such as problems with water quality, people’s health, biodiversity)
are often higher than with organic farming.
[2]
If these costs were borne by
conventional producers instead of by taxpayers, at least some of the costs would
be passed on to the consumer, thus reducing the difference between retail prices
for products of the two farming methods.
Another way in which (farm)
prices can be reduced is by subsidies for organic production. They are provided
in some European countries. The effect may be that the cost of production is
lowered, and that the farmer can accept lower product prices in order to
survive. This can be passed on to the consumer.
To obtain price premiums, organic
products need to be certified as genuinely organic. In some countries
certification is rather straightforward, as the infrastructure is in place. In
others, any certification and especially one that is acceptable to enable
international trade, can be a major problem, and rather costly.
Another issue is the availability
of the market. Campaigns in favour of “domestic consumption” can enlarge the
market for some producers, and restrict access for others.
So, in summary, separate marketing can be rather
expensive for several reasons, including the low volume of product, the
possibility of monopoly power in the trading sector and the requirements of a
certification system. The taxing of pollution-causing inputs in conventional
farming, and subsidies for organic farming can reduce the differences in
consumer price for organically and conventionally grown products. Costs of
certification to secure the possibility of (international) sales, possibly
through international certification, can be a major problem (and very costly).
An additional cost for producers in exporting countries is that they may have to
fulfil the requirements (and organic standards) of several countries
simultaneously. A separate problem for those countries is that the organic
movement, especially in developed countries, may be focussed on local
consumption, thus making market access for exporting countries more difficult.
Producer
constraints in developing countries
A list of
production constraints for developing countries closely resembles the problems
applicable to organic farmers in general (Twarog and Vossenaar 2002):
·
technical
know-how (due to few trained professionals in the field);
·
lack of organic
production inputs (composting materials, biopesticides, biofertilisers);
·
lack of
labour;
·
little research
and development (varieties and production methods);
·
conversion
method, with reduced yields, may be a larger obstacle than in developed
countries;
·
infrastructure
problems (e.g. transport and storage)
for regular agriculture makes segregation of organic production even less
likely;
·
limited market
information and channels;
·
lack of
acceptance by existing standards and certification, or the need to import
certification expertise in order to be able to export.
A further issue
of relevance to farmers who do not own their land, possibly more frequently the
case in developing countries, is investment in soils. In organic agriculture,
the emphasis is on soils, where improvements are seen as essential for nutrient
and pest prevention management. In those countries where farmers own their land,
or where leasing arrangements are such that land cannot be taken away from the
user easily, investment in the land base is not a problem, as the returns are
for the investor. However, where the farmer has no land-tenure, there is no
incentive for the lessee to improve soil quality. Indeed, there may be a
disincentive, as improvement of land quality may be directly linked to the land
being withdrawn from the user.
When
listing producer constraints, it is important to realise that some issues relate
to the scale and maturity of the industry, and will be resolved as the industry
grows. That is, these problems are not intrinsic to the organic system, even
though farmers may experience them as problems for the time being. For example,
lack of information about organic practices is often mentioned as a major
problem to convert to organic agriculture. Whereas this may be a problem for
many prospective organic farmers at present, if future generations on organic
farms continue to farm organically, a lot of the knowledge will be automatically
transferred between generations — and to non-organic neighbours. Another
example is the market for both inputs and outputs. There is no reason to believe
that the markets for organic inputs, at least the physical ones, will behave
differently from those operating for conventional farmers. The costs of
processing and marketing organic produce should also decrease per unit of
product, as the number of organic farmers increases. An increase in the number
of traders could reduce the scope for monopoly rents. Finally,
many of the
problems that are genuine long-term problems for organic agriculture can be
alleviated by government policies. This is the topic of the next
section.
Justification
Some
countries realise that there is a role for government to play in the expansion
of organic agriculture. As negative externalities in conventional farming are
larger than in organic agriculture, they have decided that at least some
government interference favouring organic agriculture (or adjusting the balance,
some would say), is justified.
Inputs
in organic agriculture often possess more of the public goods characteristic
— a justification for government involvement — than in conventional
farming. Changes in rotation, crop and livestock mixtures, biological processes
involving predators and parasites etc. take the place of pesticides and
fertilisers — private goods for which companies are willing to do research
and advertising. Therefore, without government intervention, obtaining and
dispersing knowledge about the most efficient use of many of the practices in
organic agriculture will be carried out at a sub-optimal level. Also the
development of a separate market, requiring standards and certification both for
the domestic and international market, has public good aspects, and deserves
government attention. Policy measures are therefore usually in the areas of
subsidies for organic farmers, taxes for conventional farmers, research and
extension, and product certification and
harmonisation.
The
last policy mentioned in this section refers also to markets. However, it is
mainly a private initiative to influence the market availability for domestic
producers.
Level
of support
Agriculture
is carried out rather intensively in many European countries, and population
density is such that any negative effects of such farming would perhaps be felt
earliest and most intensively by inhabitants/consumers in those countries. In
addition,
In
the
Although organic growers in other
countries may well receive some support in one form or another, it will rarely
be to the extent provided in
Subsidies
for organic growers
Organic
farm subsidies have a number of direct and indirect effects. First of all, they
allow farmers to sell their products cheaper than they otherwise could have
done. This will affect the number of consumers who are willing to buy the
produce, a very important aspect in building a market. At the same time, it is
likely to affect the input prices into the production process, especially of
land. This is the case because there is a conversion period for organic
production, i.e. a threshold to
entry. However, the price is not likely to rise too much, as other land can
— in most cases — readily be converted to organic farming. The net effect
for organic farmers is therefore an increase in income, depending on the price
effect.
In
countries where conventional farming is subsidised, (unintended) negative
effects on organic agriculture by these general subsidies can occur. For
example, due to a difference in crop mix on organic and conventional farms, EU
policies (which pay different amounts for different enterprises) can deliver
higher subsidies to conventional farms than to organic farms of the same size.
This was the case, for example, in
A
second class of effects is created towards producers who do not receive
subsidies. If they have similar costs to producers who receive subsidies, they
will become less competitive, and may go out of business. This was recognised in
the
Farm
subsidies in general can lead to inefficient use of resources, in organic
agriculture as in conventional agriculture. In other words, subsidies in one
country, by affecting the price level and the quantity of production (number of
farmers who can stay in business), affect farmers in other countries. This can
distort the true picture of efficiency in resource use between organic farmers
in different countries: bad news from an environmental
perspective.
The
international organic movement presses for subsidies for organic agriculture, as
this is its role. But these subsidies may have an indirect effect of limiting
production in non-subsidised areas. It is important to realise that organic
farmers in those countries are equally farming according to organic practices,
and deserve as much support by those who are concerned about minimising the
world’s use of resources in the quest for agricultural production. A more
appropriate approach may therefore be to target the externalities generated in
conventional farming.
Taxes
on conventional farming methods
The
market solution to the problem of ensuring that conventional farmers take more
responsibilities for the externalities they cause is, in theory, reasonably
straightforward, e.g. taxing the use
of fertilisers and pesticides such that producers only use the amount of input
that causes damage equal to the taxes paid. Scandinavian countries in particular
have implemented such policies. For example,
If
the intention of taxes is to make farmers carry the burden of the total cost of
the input, the practicalities of a tax are not quite clear. As fertilisers and
pesticides have different effects on different soil types and under different
climatic conditions, the use of the same amount of the same input does not
create the same environmental damage. Making each farmer pay their particular
cost is therefore difficult, and an assumption of average costs in cost
calculations may therefore be most appropriate.
Research
and extension
Lack
of funding for organic research and extension is often pointed out, and the
direction of research to promote organic agriculture has also been the topic of
discussion.
[7]
In the past, the emphasis of research has often been on farm production
techniques. For example, at the International Federation of Organic Agriculture
Movements’ (IFOAM) Scientific Conference in 2000, almost half of the papers (and
three‑quarters of the posters) were presented under production-related headings
(soil, plants, animals). Approximately 15% of the papers were in the market
development category (including standards and certification) and a similar
figure for policies.
Very
little effort has gone into analysing where the limited funding could best be
spent to reach the goal of expanding organic agriculture (Wynen and Vanzetti 2000). One area
that has been recognised as worthy of attention for example is that of consumer
education, for example in
Research
into more efficient use of inputs into organic farming will result, in the long
run, in lower farm-gate prices, not in higher returns to farming. This means
that, in an indirect way, fewer problems with production techniques result in
decreased production costs, which are then passed on to the consumers.
Standards,
certification and harmonisation
Product certification is an
essential part of the viability of organic producers, and is important in
international trade. Some countries,
for example in
Despite the organic movement’s
professed interest in local consumption of organic products (see below), there
are a number of countries where exports are and will be of great relevance. In
developing countries, export markets are essential for income generation,
especially where premium prices can be secured in developed countries and less
so domestically. In other cases, such as
In
order to facilitate international trade, harmonisation of standards and
certification over the world is needed.
[11]
This should not imply exactly the same standards for all countries. As
agricultural conditions are dissimilar, flexibility in standards is required.
IFOAM certainly recognises this.
[12]
However, for countries to be able to export to importing countries, their
standards will need to be acceptable to the importing country. This may mean
that standards need to be adopted which are not practicable to the exporting
country. International trading rules permit countries to determine their own
standards so long as they apply them equally to imported and
domestically-produced goods. However, there is a danger that countries set
particular standards to protect their own producers.
The two countries with the
largest demand for organic produce, the EU and the
EU regulations regarding imports
have been in place since the early 1990s and are summarised here to provide a
picture of the constraints for countries wishing to export to the EU. The EU
allows three methods of import from third countries (Commins and Kung Wai 2002). First
of all, the EU established a “third country” list, which includes countries
with which the EU has established equivalence. That is, products exported from
those countries as “organic” are accepted as such by the EU.
At present, seven countries are on the list.
[13]
Products from other countries
can be imported if the importer submits documentation that the products
are produced and certified according to rules equivalent to those of the EU.
This provision (the “importer
derogation”)
is scheduled to expire on
The
For producers in many developing countries, and
also in developed exporting countries, these requirements mean that export of
organic produce may not be easy. Many developing countries do not have a
domestic organisation that can carry out the required certification.
Certification by international certification bodies then becomes essential,
which is likely to be expensive. This may be an insurmountable problem,
particularly for small-holders in developing countries. The need to comply with
different standards in different markets would add to the cost of production and
marketing. In addition, time delays, due to the requirement of documentation of
each consignment, may well inhibit exports.
Market
availability
Although rumblings about local
production and consumption have been heard for a long time in the organic
movement, they have increased in intensity over the last few years. The idea
behind it is that local consumption would cut down on transport costs, and
therefore be better for the environment (Geier 2001). While organic organisations may campaign
for consumers choosing locally produced food,
[14]
the case for reduction in resource use through
producing goods as efficiently as possible (through specialisation of production and international trade) seems
forgotten or misunderstood (Vanzetti and Wynen 2002). Purchases of locally-produced products at
higher prices than those which international trade allows, can accentuate
non-optimal resource use to the detriment of people — and
environments — in all countries. The concept of the “whole life cycle” evaluation in terms of resource
use is well established (Meier-Ploeger, Kjer and Simon 1996), yet the importance is rarely
mentioned when the issue of local food consumption comes up. Furthermore, exports of organic
goods provide an important opportunity for many poor farmers in developing
countries.
4.
Conclusions
Concerns
facing organic producers can be divided into two main groups. One is in the area
of production (inputs with their effects on yield and total production) and the
other is marketing (product prices, cost of marketing and market availability).
In the early days, the production problems of farmers were emphasised, and
research topics were often concentrated on soil, pests and diseases. More
lately, as international trade of organic products has grown, the importance of
market-related issues has come to the fore.
Direct
subsidies to organic farming, to aid conversion or to compensate for more
environmentally friendly practices, and other forms of subsidies, have been
obtained in some countries but not in most. These cause advantages for some
(including producers and consumers) and disadvantages for others (producers in
exporting countries whose competitive edge decreases). Decreases in consumer
prices are essential for a growth in the organic market, which will partly
happen through increased production and maturity of the market. A further
realisation is the need for harmonisation and equivalence in agriculture.
Serious issues regarding non-tariff barriers (such as time delays due to the
need for documentation for importing purposes) are raised. A push towards
domestic consumption seems afoot, which could also be seen as a non-tariff
barrier: organic producers in some developed countries protecting their patch
against products from exporting countries.
Rather than dividing the organic movement through
promoting policies that are good for some and bad for other producers, a more
useful approach for all organic producers may be to encourage governments to
initiate polluter-pays policies. A tax on pesticide and fertiliser use is one
such example in agriculture. Though several countries in
Commins, K. and O. Kung Wai (2002), “Regulations of imports into major markets” in Harmonisation and Equivalence in Organic Agriculture, IFOAM Conference on Organic Guarantee Systems, Nuremberg, Germany, February.
FAO [Food and Agriculture Organization of
the United Nations,
FAO (1998), “Evaluating the potential
contribution of organic agriculture to sustainability goals”, FAO’s technical contribution to IFOAM’s Scientific Conference,
FAO (2000), “Research methodologies in organic farming: on-farm
participatory research”,
REU Technical Series No. 63,
Geier, B. (2001), Ecology & Farming Magazine, No. 26:www.ifoam.org/orgagri/regionalseasonal.html.
IFOAM (2002), International Harmonisation and Equivalence in Organic Agriculture, Conference on Organic Guarantee Systems held by IFOAM in co-operation with FAO and UNCTAD, Nuremberg, Germany, February.
Jha, V. (forthcoming), “India”, chapter in Strengthening Research and Policy-Making Capacity on Trade and Environment in Developing Countries, UNCTAD, Trade, Environment and Development Branch, Geneva, Switzerland.
Krell, R. (ed.) (1998),
“Biological Farming Research in
Lampkin, N. and S. Padel (eds) (1994), The Economics of Organic Farming — An
International Perspective, CAB International,
Lampkin, N., C. Foster,
Lipson, M. (1997), Searching for the o-word, Organic Farming Research Foundation, Santa Cruz, California, United States of America.
Lohr, L. (2001), “The importance of the Conservation Security Act to US competitiveness in global organic markets”, Faculty Series 01-19, Department of Agricultural and Applied Economics, University of Georgia, United States of America.
Meier-Ploeger, A.,
Michelsen, J., U. Hamm,
E. Wynen and E. Roth (2000), “The European
Market for Organic Products: Growth and Development”, report commissioned by the
European Commission,
Offermann, F. and H. Nieberg (2000), “Economic Performance of Organic Farms in
Pimentel, D., H. Acquay, M. Biltonen, P. Rice, M. Silva, J. Nelson, V. Lipner, S. Giordano, A. Horowitz and M. D’Amore (1993), “Assessment of environmental and economic impacts of pesticide use” in D. Pimentel and H. Lehman (eds), The Pesticide Question: Environment, Economics and Ethics, Chapman and Hall, New York, United States of America, pp. 47-84.
Redman, M. (1996), Industrial Agriculture: Counting the
Costs, Soil Association,
Schou, J. and J. Streibig (1999), “Pesticide taxes in
Soil Association (2002), “Response to NFU
survey of organic farmers”, Press Statement, 25 July: www.soilassociation.org/sa/saweb.nsf/848d689047cb466780256a6b00298980/80256ad80055454980256c010045b622?OpenDocument
.
Stolze, M., A. Piorr, A. Haring and S. Dabbert (2000), “The Environmental Impacts of Organic
Farming in
Twarog, S. and R. Vossenaar (2002), “Obstacles facing developing country exports of organic products to developed country markets” in IFOAM, International Harmonisation and Equivalence in Organic Agriculture, Conference on Organic Guarantee Systems held by IFOAM in co-operation with FAO and UNCTAD, February, Nuremberg, Germany.
UNCTAD (2003), Strengthening Research and Policy-making
Capacity on Trade and Environment in Developing Countries,
Vanzetti, D. and E. Wynen (2002), “Does it make sense to buy locally produced organic products?” in Hall, D. and J. Moffitt (eds) Economics of Pesticides, Sustainable Food Production and Organic Food Markets, Elsevier, pp. 195-208: www.elspl.com.au/abstracts/E2.htm.
Wynen, E. (1992), “Conversion to Organic Agriculture in Australia: Problems and Possibilities in the Cereal-Livestock Industry”, report funded by the Rural Industries Research and Development Corporation, National Association for Sustainable Agriculture, Australia. A summary can be found at: www.elspl.com.au/abstracts/CONVERSION.HTM.
Wynen, E. (1998), Organic Agriculture in Denmark – Economic Implications of a Widespread Change, Danish Institute of Agricultural and Fisheries Economics, Report No. 99, Copenhagen, Denmark.
Wynen, E. (2000), “Bio-dynamic
and conventional irrigated dairy farming in
Wynen, E. (2001), “The economics of organic cereal-livestock farming in Australia revisited”, proceedings of the RIRDC Inaugural Conference on Organic Agriculture, Sydney, Australia, 27-28 August: www.elspl.com.au/Abstracts/abstract-a17.htm.
Wynen, E. (2003), “Organic
farming in
Wynen, E. and D. Vanzetti (2000), “Research in organic agriculture -
Assessment and future directions” in David, C., G. Allard and
J. Henning (eds), Organic Agriculture Faces its Development:
the Future Issues. 12èmes
Entretiens Jacques Cartier ISARA — Université LAVAL-INRA: www.elspl.com.au/Abstracts/abstract-g4.htm
.
[1]. FAO (1998): “Due to slow mineralization of nitrogen under cool growing-conditions, crops on organic farms have a shortage of nitrogen early in the season. However, in countries where low soil temperature is not a limiting growth factor, as in many developing countries, this factor should not prove significant.”
[2]. See, for example, work carried out by Pimentel et al. (1993); FAO (1996); Redman (1996); Stolze, et al. (2000).
[3]. See also Lipson (1997).
[4].
Luanne Lohr, Associate Professor Agricultural
and Applied Economics,
[5].
“The AQIS organic program will directly cost the Australian organic and
biodynamic industry A$84,500 (approx. US$46,500) for the 2002-03 financial year.
This sum is divided into seven certifying bodies…and I assume is then passed
onto approx 1 700 clients
[6]. In general, the government tops up farmers’ research levies. If this is added to the levies on organic farmers, the total amounts to USD 360 000.
[7].
See, for example, Krell (1998);
FAO (2000); Lipson (1997); Lockeretz (2000); and Wynen and Vanzetti
(2000).
[8]. See, for example, Wynen and Vanzetti (2000), and Lampkin et al. (1999).
[9]. Lampkin et al. (1999).
[10].
There are countries where a large
part of the organic production is sold in the conventional market. For example
in
[11]. See IFOAM (2002).
[12]. See IFOAM’s website: www.ifoam.org/standard/basics.html under “Variations in Standards”.
[13].
[14].
See press release by the Soil Association,