Le Dossier de l'environnement de l'INRA n°22  
D22 : INRA faced with Sustainable Development : Landmarks for the Johannesburg Conference   

Should French agricultures grasp on the environmental opportunity?

1. The fundamental assets of French agricultures are still going strong
2. However the vulnerabilities of production systems are worrying
3 Taking Advantage of the Assets of French Agricultures in a Necessity to overcome their Vulnerabilities
Conclusion: taking the right direction

Box 1: Indicators for the Integration of Environmental Concerns into the Common Agricultural Policy
Box 2. OECD agri-environmental indicators, 27/11/2000

Bibliographical references


For France and the European Union, the agricultural issue represents far more than its share in the gross domestic product (GDP) and demography. It is also at the base of food security, a major feature of its international image, a key file for its political credibility, as well as a source of trade surplus, a major financial stake as regards the CAP (Common Agricultural Policy), an essential land management and resource management tool and, perhaps, the touchstone of motivations for its extension to Eastern countries. It seems to be an established and accepted fact that agricultural products should not be viewed in the same way as raw products such as metal or petrol, at the mercy of speculation, but that their production and price must be sufficiently stable to ensure their regular supply. Besides, climatic change confers to them a new dimension.
This is the reason why current uncertainties demand a strategic analysis of the assets and vulnerabilities of the "French farming enterprise" (as some call it, although this includes a widely diverse types of agriculture), from the angle of context and prospects. This is all the more important as, in spite of the diversity of production systems, products and terroirs, the farming world is considered as a single whole by French as well as foreign citizens and consumers.
Our paper, therefore, does not propose to deal with the future state of energy in 2020 or 2030, nor with environmental analyses, although everyone is aware of the socio-economic impact of observed or predictable damage, but will mainly concern economic suggestions stemming from three observations.

[R] 1. The fundamental assets of French agricultures are still going strong

These are multifold.
Since 1995, agricultural commodities contribute to ranking the French farming industry second in national trade surpluses, mainly thanks to finished products. The situation is in total contrast to that of Japan, a major net importer (1), or New-Zealand, whose economy significantly depends on its agricultural exports (2).
The EU domestic market absorbs 70% of French exports, a major factor of stability, and Europe as a continent totalling 450 million inhabitants is by far its main market
The diversity of production systems, products and terroirs is a national weapon against the trivialisation of agricultural products that compete against each other only through the price factor, thus driving prices lower and lower down. The specialists are the only people who seem to be aware of this diversity: who knows that the Institut de l'Elevage (the French livestock institute) describes 11 different ways of producing cow milk in Brittany and 18 ways of producing cattle meat in the Limousin region?
The national and international image of agricultural products (tradition, life style, quality, savoir-faire, subtlety) was a major issue up to now. The recent major crises (dioxin, but more especially the BSE and foot-and-mouth epidemics) do indeed affect French agriculture as a whole, although this is not specific to France.
The agricultural community has already demonstrated that it is able to respond and reorganise when faced with new challenges, as long as the course to take is clearly defined. Why should this not be the case, once again?

[R]  2. However the vulnerabilities of production systems are worrying

These vulnerabilities relate on the one hand to the structure of agricultural fabric, and on the other hand, to the relationship between agriculture and the territory it uses.
Help is oriented in such a way that an increasing share of all national agricultural productions and development structures are focussed on basic products that have no intrinsic or territorial specificity. These commodities are "massified" and highly susceptible to intra-European and even international competition due to their price: this is the case for certain cereals and for meat and dairy products. This situation mirrors that of the textile and the iron and steel industry 25 years ago. All this type of animal production (especially pork and poultry) is being delocalised to lower labour costs. This situation is not economically viable so long as the cost of international transport remains as low as it currently is (the link with the policy on climate change is obvious). Even though the nature of the BSE and foot-and-mouth crises is different they resulted in a cruel fact - the shift of demand to other productions on the European domestic and foreign market.
The disparity of situations and composition of income (0 to 80% of direct income is derived from public subsidies, depending on the type of activity - according to the data published by the French Bulletin d'information du ministère de l'Agriculture-BIMA) is making professional solidarity artificial and has created widely diverging individual interests. This weakness is increased by two factors:
- the upstream dependence of the agricultural community on the agrifood industry and the banks, and its downstream dependence on large retailing chains. This dependence is even greater for non-characteristic products that can only be differentiated by the brand mark of the agribusiness firm or that of the retailing chain.
- the increasing difficulty for young farmers to enter farming (due to the farm size and the steep rise in prices in some regions) to the advantage of a systematic and often locally favoured extension of farms.
The environmental damage suffered by several leading agricultural regions of France is having a high cost (for example, some households pay roughly 400 euros/year for purification of water by the commune and yet still have to drink bottled water), and has sometimes become unbearable for the inhabitants and activities of the area (the quality of common resources such as water, air and soils is often far too degraded: this can lead to economic problems and withdrawal of quality labels for dairy farms, shellfish farms, breweries, etc.). The situation sometimes becomes critical for the farming activity itself (health of farmers, contamination of crops and livestock, impossibility to respect specifications, soil fertility sometimes threatened in the short-term, local social acceptability weakened, etc.).
The discrepancy between the traditional representations of agricultural fairs and agribusiness marketing and the facts revealed by the media on production techniques reinforces the shock and rejection caused by information on dioxin, chemicals or BSE. Consumer opinion shows that strengthening the link between agricultural products and the land on which they are produced is perceived as a reassuring factor and respect for environment as an ethical sign of respect for the consumer.
The effects of BSE and foot-and-mouth disease have accelerated this evolution and financially, commercially and politically induce us to envisage a major reorientation of agricultural policies in the short-term, as planned in the Marrakech Agreement and the 2000 Agenda, in the context of expanding the EU.

[R]  3. Taking Advantage of the Assets of French Agricultures is a Necessity to overcome their Vulnerabilities

The World Trade Organisation (WTO).
The "peace clause" included in the Marrakech Agreement is due to expire at the end of 2003. It calls into question most European public support to agricultural production ("red boxes" and "bleu boxes"(3)). This is not the case for the so-called "green" box. Its political legitimacy rests on the issue of food security for each region of the Globe and income insurance for farmers, as well as on the environmental problems encountered across the planet. This field is increasingly documented and even quantified although unequally according to the topic addressed (the level of phosphorus and nitrogen far more than that of biodiversity, for example), and this confers a particular place to the environmental features of production systems.
The indicators elaborated by the Organisation for Economic Co-operation and Development - OECD - (see Box 1, below) supply these negotiations with common qualitative and quantitative references (description of situations, thresholds, priority issues, etc.). For example, these documents show that it was, above all, the average income of French farmers that increased the most between 1986 and 1998.
National interventions reflect, often in a documented and quantified way, the main concerns of the States and comparative advantages of their production systems, especially regarding their environmental characteristics. For New Zealand, for instance, a good indicator of nitrogen use would be the percentage of grasslands in the useful agricultural area (UAA).
It is not easy to find concrete and validated data providing a clear and comprehensive view of this field: they are extremely accurate on some points, but are more generally scattered, often stem from investigating other issues, or are too recent and thus lack statistic or temporal distance. The case of France is not unique, but the country's economic situation translates into vulnerabilities and thus induced demands. Even if we were to count on a likely bilateral agreement between Europe and the United States before the plenary negotiations, any weakness in the European strategy would be exploited, in particular in front of the developing countries.

On paper, the US situation is indeed far more favourable as regards the environmental issue than that of the EU: 20 to 25% of US direct aid is motivated by environmental measures, against roughly 5% for the EU. This does not mean that in the US agricultural practices are environmentally more virtuous than in Europe, but that their arguments on this issue are more easily shared with other States around the negotiation table.
As regards agricultural income, which also intervenes in the debates on the "green box", the statistics published by the OECD show that France was way ahead of other countries between 1990 and 1995, with an average real growth of 8%, as compared to 5.5% for Denmark, 0.5% for the USA, 0% for the Netherlands and -1.5% for Canada. Support to producers, in terms of percentages of the average gross income of farms, has decreased over the past 15 years in all the countries quoted by OECD, except for Mexico and Norway, where they have increased, and for the European countries, where it has remained stable. While financial support per farmer is slightly higher in the US, support per hectare is 9 times higher in the EU(4). Of course these are only averages with a wide statistical dispersion. But the international effect is guaranteed: no use trying to arouse the pity of negotiators on the fate of the "average French farmer", or using this data to prove that the 1994 agreements are being properly implemented in Europe…

The Common Agricultural Policy (CAP)
Regarding the EU, the proposals made by the member States also reflect their strategic positions on agricultural structures and options. Indeed, the 2003 WTO negotiation will occur at the same time as EU enlargement and redeployment of the little flexible CAP budget. Extending the present regime to Poland, Hungary, Czech Republic and Slovenia would increase the CAP budget by a yearly 15 billion Euros, for a total of 42 billion Euros, and thus cannot be envisaged. The French lion's share of the budget is obviously coveted. In this context, it is crucial that we underscore the agri-environmental assets of a diversity of French agricultural systems (and by the same token recognise and correct the excesses of others), since they represent a major diplomatic argument. If we do not, then the credibility of France and its future financial returns would become highly endangered.
The evolution of consumer and societal demand to the agricultural world, stepped up by the BSE crisis, is also reflected in the specifications imposed on producers by the large European retailing chains (EUREP(5)). Here are some recommendations: no growth-promoting antibiotics; traceability of genetically modified animal foods; meters and water-economising schemes for irrigators; analysis of nitrogen, phosphorus, heavy metals, fertilisers and other pollutants in irrigation water before use; compulsory and relevant training of people handling agro-chemicals, and their assistance by certified advisors, etc.
Everything thus converges towards changing the rules of the game. Several recent Community documents (especially COM 2000(20) - January 2000; see Box 2) enlarge on the future orientations of this game, which are confirmed by current on-going discussions. Studies on the environmental characteristics of production systems in OECD or EU countries, all underline the 2002-2003 horizon, i.e. the end of the "peace clause".

[R] Conclusion: taking the right direction

French agricultures must take into consideration this profound evolution if they are to overcome their own vulnerabilities. They must also take advantage of their own assets in the new context, characterised by a strong convergence between societal demands relayed by agribusiness and the evolution of political discourses in the framework of WTO and CAP. Protection of natural resources, of the soil capital and of human health does not sum up the full scope of agricultural policies but will orient them considerably. On this point let us remember the statement made by OECD's director of Agriculture, G. Viatte, when concluding the WTO and Agriculture seminar (SFER-INRA  (6)) on 6-7 February 2001: "environmental policies will perhaps have a stronger impact on agriculture than agricultural policies".
This analysis is nothing new: it was already around at the beginning of the 1970s (CENECA (7), 1971, for example) when it was chiefly upheld by academics and associative actors. They were rarely listened to for the following… thirty years! Farmers are increasingly becoming aware of this situation and of the lack of structured and clear directions to support them. Their concern rapidly turned into disarray with the shock of the BSE and foot-and-mouth epidemics. If the guidelines were as clearly as in the 1960s, the agricultural world would doubtless (not alone, but extremely actively) efficiently reorganise its techniques, training, representations of its social roles and thus of its own image and that of its products. Farmers would therefore benefit from competition conditions no longer exclusively dictated by prices, but would also be less vulnerable to delocalisation. Their image and income would be more autonomous and their social significance enhanced.
To do so, the country (and at its level, Europe) must do the same as all economic sectors that wish to maintain and increase their commercial and social recognition in terms of quality and quantity: the country must create the proper conditions for promoting a qualitative leap conform to the economic, commercial and physical perspectives of the century. This would, for example, entail:
- sufficiently diverse and renovated technical training to make as much room as possible for progress and adaptability to the various ongoing changes (consumer demands, climate evolution, pressures on water and soil resources, new forms of qualitative competition);
- a strict framework for repressing fraud and promoting quality innovations, which on the one hand, protects those farmers who respect their clients and society against competition-induced distortions, and on the other hand, increases the recognition of efforts made by the agricultural community, thus enabling them to benefit from a larger share of added value. Claims for acknowledgement of quality and protection of "black sheep" are incompatible in the long run;
- further opening of the agricultural world to collaborations and confrontations with its contemporaries, an essential factor of adaptability and credibility;
- a discourse valorising nationally and internationally the farmers' work, their good farming practice relative to the resources they work with and the carefully monitored anchoring of the products they supply in the local territory; this would once again enable France to spearhead European evolutions;
- the defence by the EU as a primary concern of food security and the just remuneration of quality in material and immaterial agricultural goods, required by the European clientele, especially for finished and quality products which bring in net commercial surpluses. A credible and coherent national assessment and monitoring system would guarantee France's position in the European Union, in the CAP-WTO context;
- an international role reinforced by this internal coherence for solvent clients; for the others, this role consists in food aid, and comes under a different policy;
- and, last but not least, a public research system that confirms these new directions as stated for instance by the French National Institute for Agricultural Research (INRA): "preserving the environment and producing sustainably" and "adapting species, practices and systems to changing contexts".


This article is taken from the "Courrier de l'environnement de l'INRA, n°43", by D. Dron.
Translated from French by Nicole Scott.


[R] Box 1:
Indicators for the Integration of Environmental Concerns into the Common Agricultural Policy
COM2000(20), January 2000

Agri-environmental policies(1.1.3)
"Central to understanding this relationship is the principle of "good farming practice" corresponding to the type of farming which a reasonable farmer would follow in the region concerned." (1.3.1.3)
"Farmers should respect general requirements as regards environmental care without specific payment. This means that all farmers should follow compulsory legal restrictions on pesticide use, fertiliser application, water use and where appropriate, national or regional guidelines on good farming practice." (1.3.1.3)
"However, wherever society asks farmers to pursue environmental objectives beyond good farming practice, and the farmer incurs a cost or foregoes income as a result, then society must expect to pay for that environmental service. […] This approach is based on the Polluter-Pays-Principle. Accordingly farmers bear compliance costs up to a reference level of "good farming practice"." (1.3.1.3)

CAP reform (1.3.1.4)
"Three courses of action are included in this Regulation. First, to apply compulsory restrictions. Such measures are already required in Member States in relation, for example, to pollution by nitrates in water. Secondly, Member States may apply cross-compliance, by attaching specific environmental conditions to the granting of direct CAP payments. Thirdly, Member
States may use agri-environment programmes to protect or enhance the environment beyond good farming practice."
"Society in general, although prepared to take into account legitimate social and economic interests, will not accept that CAP funding leads to environmental degradation whose cost it, in turn, would have to bear. It will be, nevertheless, necessary to carefully monitor and analyse developments in all agricultural sectors irrespective of the level of CAP intervention."

Issues for the future: environment and trade, consumer concerns, enlargement (1.3.2)
"It will be necessary to fully meet international commitments under Multilateral Environmental Agreements."

Environmental indicators must meet five criteria to be integrated in the CAP (1.4)
- "to identify the key agri-environmental issues that are of concern in Europe today;
- to understand, monitor and evaluate the relationships between agricultural practices and their beneficial and harmful environmental effects;
- to assess the extent to which agricultural policies respond to the need to promote environmentally friendly agriculture and to communicate this to policymakers and the wider public";
- to monitor and evaluate the site specific environmental contribution of Community programmes to sustainable development;
- to map the diversity of agri-ecosystems in the European Union and Candidate Countries. This has particular relevance in explaining to the EU's trading partners the specificity of the farmed environment in Europe".

Site specificity (2.5)
- "…requires a differentiated approach, reflecting regional differences in economic structures and differences in natural conditions. (The available data, often highly aggregated may provide some valuable insights, but can also be misleading for some areas such as biodiversity or water quality due to a lack of regional differentiation)"
- "…the impact of many polluting, depleting or beneficial processes will depend on the site specific characteristics such as geology, topography or climate. Finally, a site-specific approach enables us to look at ecosystems in a holistic way and address systemic characteristics such as quality and vulnerability. A meaningful systemic context of agri-environmental indicators can be provided by the concept of "landscape" as a cultivated, partly semi-natural space within which agricultural production takes place and which is characterised by the totality of its biophysical, geophysical and cultural features."

Using landscapes to classify European agri-ecosystems (4.4)
"…identify vulnerable or threatened areas… Work of this type has already been undertaken by some member states and could be extended to a Community level… From a policy point of view, at least five groups of landscapes are present across the Union in varying degrees":
"- high nature and cultural value landscapes threatened by the intensification of agriculture and where environmental quality is very dependent on strict constraints being placed on farming activity;
- farming dependent high nature value and cultural landscapes threatened by the marginalization of agriculture and where agriculture has a particular role in creating environmental quality;
- landscapes characterised by low-input farming, low pollution and resource depletion as well as the enhancement of habitats and biodiversity;
- landscapes characterised by intensive or extensive good farming practice in a balanced relationship with the land leading to the maintenance of natural resources, biodiversity and semi-natural ecosystems;
- landscapes characterised by overexploitation, pollution and resource depletion leading to the deterioration of natural resources, biodiversity and semi-natural ecosystems."
"Groups and citizens must be reassured that sound scientific knowledge is duly incorporated into the indicators." (4.5)

Agricultural activity as a biophysical activity (2.3)
- "A second specificity of agriculture is that by its biophysical nature it is part of, rather than external to, local ecosystems."
- "It is particularly important to develop indicators that capture the key trends in farming activity: expansion-withdrawal, intensification-extensification, specialisation-diversification, marginalization-concentration, available at a range of geographical levels."
ELISA-Environmental Indicators for Sustainable Development: 22 state indicators (soil, water, air, biodiversity, landscape), 12 pressure indicators (ECNC-European Centre for Nature Conservation, Netherlands).
- "Four main indicators to assess the environmental state were retained (biophysical adequateness of land use, openess versus closedness, adequateness of key cultural features, and land recognised for its scenic or scientific value."

Headline indicators (4.6)
Factors ad responses influencing farming practices Enhancement beyond good farming practice Expenditure/area on agri-environmental programmes
Farming practices Rational input use Pesticide use risks (factoring in integrated pest management)
Harmful and beneficial processes Benefits outweight harmful effects Nitrogen balance
Site specific state Ecosystem health Bird species on agricultural land
Global environmental impact Ecosystem richness Landscape diversity


 [R] Box 2:
OECD agri-environmental indicators, 27/11/2000

Group 1: "Politically relevant indicators in all OECD countries; non-ambiguous, measurable and easy to understand"
Use of fertilisers, herbicides, UAA energy; evolution of land use, agricultural use of space (distribution)
Total use of water
Emission of ammoniac and greenhouse effect gas

Group 2: "Politically relevant indicators in all OECD countries; not totally non-ambiguous, measurable and easy to understand"
Global management of the farm (including organic agriculture), management of fertilisers, herbicides, water, soils and space
Vulnerability to erosion (water and wind), fertility of soils, soil Organic Matter, Soil C, biodiversity of soils
Water quality and risks (N, P, pesticides, suspended matter), use and renewal of underground water
Carbon sinks
Genetic biodiversity, species biodiversity (wild, domestic and cultivated), semi-natural habitats, habitat matrixes (environments + biodiversity and spatial configuration)

Group 3: "Politically relevant indicators in certain regional groups of OECD countries, concerned with areas not covered by the other indicators"
Soil pollution due to heavy metals and chemicals, soil compaction, acidification, salinisation, basification
Landscape typology, assessment
Hydric retention capacity of soils, landslide risks
Pathogenic elements in the water from livestock farming, salinisation
Purifying capacity
Pressure on water resources due to irrigation
Invasive species


Notes

(1) 12,5% of its imports against 0,4% of its exports in 1998 (OECD).[VU]
(2) 48,5% of exports in 1998 ; whereas France has a total of 12,8% and the Netherlands 19,2% (OECD) [VU].
(3) In 1994, public aid to agriculture was grouped into three categories called "boxes": the "Red Box" consists in support to export prices, which will end in 2004 under the Marrakech Agreement. The "Blue Box" consists in direct aid to production (the aid given is proportional to the quintals produced or heads of cattle possessed and not based on productivity/hectare). This was a transitory category that was to be progressively restricted between 1994 and 2004. The "Green Box" concerns uncoupled support to production and introduces no distortions in exchanges: it is thus legitimate from the standpoint of commercial competition.[VU]
(4) For example, in US dollars/hectare in 1997-1999: 5 for New-Zealand, 36 for Canada, 85 for the USA, an average of 211 for OECD states, 801 for the EEC, 9 823 for Korea and 10 671 for Japan (OECD).[VU]
(5) www.cmi-plc.com/eurep.htm.[VU]
(6) SFER - Société Française d'Economie Rurale: French Society for Rural Economy INRA-Institut National de Recherche Agronomique: National Institute for Agricultural Research.[VU]
(7) CENECA-Centre National des Expositions et des Concours Agricoles: National Centre for Agricultural Exhibitions and Competitions.[VU]


[R] Bibliographical references

Environment
PNUE, 2000. Global Environmental Outlook 2000. Earthscan, Londres.
European Environment Agency, 1999. Environment in the European union at the turn of the century. Official publications of European Community, Luxembourg.
OCDE, EPOC (1999). Environmental Outlook. www.oecd.org/env/docs/epocppc999.pdf
Dron D., 2000. Environnement : les enjeux du prochain siècle. In T. de Montbrial : RAMSES 2001, rapport de l'IFRI (2000). Dunod, Paris, 374 p.
Dron D., 1995. Environnement et choix politiques. Flammarion (coll. Dominos), 128 p.

Agriculture
Agriculteurs et ruraux dans le monde de demain. Cahiers du CENECA, colloque international, Salon de l'agriculture, Maison de l'Unesco, 3-4-5 mars 1971, 572 p.
Indicateurs d'intégration de l'environnement dans la Politique agricole commune. Commission européenne, communication au Conseil et au Parlement, COM2000(20), 26 janvier 2000.
OCDE, 2000. Politiques agricoles dans les pays de l'OCDE, suivi et évaluation 2000, agriculture et alimentation. OCDE, Paris, 288 p.
Hervieu B., Viard J., 2001. Au bonheur des campagnes. L'Aube, Paris, 155 p.
Hervieu B., Guyomard H., Bureau J.C., 2000. L'avenir des politiques agricoles. In T. de Montbrial : RAMSES 2001, Dunod, Paris, 374 p.
Hervieu B., Viard J., 2001. L'archipel paysan - la fin de la république agricole. L'Aube, Paris, 110 p.
Pujol J.L., Dron D., 1998. Agriculture, monde rural et environnement : qualité oblige. Cellule prospective et stratégie, rapport à la ministre de l'Aménagement du territoire et de l'Environnement, La Documentation française, Paris, 589 p. (cf www.inra.fr/dpenv/pujolc37.htm).
Environmental economy
Cohen de Lara M., Dron D., 1998. Évaluation économique et environnement dans les décisions publiques. Cellule prospective et stratégie, rapport au ministre de l'Environnement, La Documentation française, Paris, 400 p.
(cf www.inra.frdpenv/cohenc33.htm).

[R]