Alvarez, Pablo

Suárez Cardona, Francisco

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Action and instruments for EM, steppe habitat conservation Francisco SUÁREZ^ & Pablo ALVAREZ'^^ ^Dpto Interuniversitario de Ecología. Facultad de Ciencias. Universidad Autónoma. E-28049 Madrid. Spain. "^"^PROYMASA. Tutor, 3, duplicado, r D. E-28008 Madrid Spain. mm (f*s5i>...... *r^ ES RENCONTEES DE UAGENCE REGIONALE POUR UENVIRONNEMENT PRO VENCE-ALPES-COTE D'AZUR Abstract Conservation problems and BU actions affecting Mediterranean steppes are ana-lysed. Cropland afforestation (R.2080/92/EEC), olive and almond plantations and large-scale infrastruciure, all partially subsidized by BU funds, are drastic changes that affect large áreas. Crop intensifícation via new imgation schemes and farm mergers, partially fun-.ded by FEOGA-Orientation, can also ; have serious repercussions. Conservation acíivities via ACE-Biotopes and LEFE have been useful for publicizing and dynamising the process, but compared with the áreas actually protected, they have had little effect. The paper concludes that steppes must be conser-ved in a múltiple approach, trying to combine agricultural, infrastnicture and conservation policies to the greatest pos-sible degree. Introduction In their broad definition, pseudosteppes embrace both landscapes with low natu-ral vegetation and an absence of a deve-loped shrub and tree strata and also extensive cereal croplands (Suárez et al. 1992). They cover large áreas in the Mediterranean zone of the BU. Using the declared IBAs (Grimmet & Jones 1989) as a reference, Spain (2,057,(K)0 ha) has the largest áreas, but France and Portugal (59,000 ha declared IBAs in both) and Italy (33,000 ha) also have considerable zones. Farm intensifícation since the 1960s has caused several types of profound changes to the pseudosteppes in different regions and zones. The most disadvanta-ged zones have witnessed a process of aop abandonment and regeneration into scnib (e.g., in Pugglia, Italy and the pára-mo uplands of Castilla-León, Spain- see Majoral 1987, Guüérrez et al. 1993). In other áreas such as in the Ebro valley and some irrigated parts of Extremadura, Spain (De Juana et al. 1993), there has been profound intensifícation. The regis-tered trends are, however, hard to extra-pólate into the fiíture due to the large degree of uncertainty for dryland cereal farming. This paper analyses the conservation problems for the EU pseudosteppes and the Union action and instruments that affect them. Major changes of uses There are three basic changes in use that have profound efifects on pseudosteppes: afforestation of cropland, increased tree crops on dryland, and new infrastnicture. The forestation of cropland is a valid altemative for many cereal farmers in disadvantaged zones (Regulation 2078/92/EEC). In Spain there are 1,275,000 ha of land (Sumpsi 1995) with low cereal output (less than 1500 kg/ha) and extremely low fínancial yield (see Naveso & Fernández 1993). In the 1993-1997 period, the Forestation Plan en\i-sages action in 715,000 ha. It is therefore logical to expect that these disadvanta-ged, agriculturally unintensifíed áreas which generally have high natural valúes, will be the ones that receive this aid (Castellano & Cifuentes 1994). To date, farmers have expressed less interest than expected, although this is probably transitory due to the high sunflower sub-sidies at the start of the 1990s and the cereal output of recent harvests. The área of dryland tree CTops, particu-larly olive and almond, have varied greatly due to the changes in the CAP orientation in the sector At the start of the 1980's, the EEC provided incentives for uprooting large áreas of marginal olive groves in the south and centre of the Iberian Peninsula (Pastor & Humanes 1991). This trend has been reversed in recent years, with plantations of olives and almonds on many pseudosteppes in the S and SE of the Península, piniarily in Andalucía. One clear example of this process is the trend in the Andalusian municipalitíes of Jodár and Cabra del Santo Cristo (Jaén). A comparison of the 1977 and 1994 Agriculture, Fishing and Food Ministry farm census in Jódar reveáis a 21% increase in área of dryland olive groves and a 37% in olives under irrigation, while herbaceous crops have declined by 53% and 62% respectively. In the second municipality, dryland olives have remained stable, while the irrigated área has risen by 303%, and herbaceous or fallow crops have fallen by 5% and 13% under each system res-pectively. Today, olives are a relatively competítive crop. There is no suiplus, they are not subject to the cuirent CAP refonn, and there are large subsidies for oil produc-tion wMch are reflected in acceptable olive paices. Furthermore, it is an altema-tive crop to cereals in some regions, especialiy zones where drip irrigation is viable, where production has increased by 50-100% (Pastor & Humanes 1991). The conversión of Iberian steppes into ohve groves has serious consequences for steppe fauna and vegetation (see Muñoz-Cobo 1992). The new olive groves are intensifíed crops that use large amounts of fertilizer as well as herbi-cides to ccMnbat weeds. Hiis causes the disappearance of the characteristic pseu-dosteppe vegetation and the replacement of the local open land fauna communities by forest types. The third problem is the creation of new infrastnicture. Most of the new works carried out by the Spanish Government, primarily highways and large dams, have been financed by structural funds. These works affect considerable áreas: in 1992-93 alone, the central Government built 1,500 km of highways, which, assuming a mínimum band width of 230 m, means that around 15,000 ha/year are affected, 185 COLLOQUE BIO'MES 1995 part of which is in steppes. The Community Direcüve 337/85/EEC obliges an Environmentai Impact Study for these new works. As severa! authors have pointed out, however (Milara 1995, Oñate et al. 1995), the quality of these studies is poor, as most focus on correcti-ve measures. The lack of EU monitoring of the Environmentai Impact Studies impedes their effectiveness in terms of limiting impact, and serious disturbances in very important natural áreas continué to occur, many in pseudosteppes. Crop and grazing intensifíca-tion Crop intensification on Iberian dryland farms is reflected in increased irrigation, farm mergers and a reduction of long-term fallow land. The first two are partly subsidized by FEOGA-Orientation, although tlieir problem is different. Irrigated land has increased steadily Spain over recent decades to 3,208,000 ha in 1992. This rise has differed by regions, as some cases such as the Ebro valley or Castilla-León are large-scale schemes promoted by the central or regional Govemments, while otliers are prívate initiatives, involving a heavy development of greenhouse crops in SE Andalusia (see Manrique & De Juana, 1991 for the case of Almería). Although the most recent predictions are for a fur-ther 600,000 ha under irrígaüon, tlie drought over the last three'years and conflicis over local and inter-regional use of water reserves are causing a conside-rable reduction in figures, and no indica-üve figures can be advanced at present. Nevertheless, increased productivity from the introduction of irrígation (cereal production practically doubles and sugar beet triples) means tJiat this tendency is possibly transitory, and in üie near future we may well see furtlier increases in irri-gated áreas. Farm mergers are being encouraged by tlie central Government and partially fun-ded by FEOGA-Oríentation. Alüiough this has already happened in most steppes, a further 300,000 ha are expec-ted to be merged in the coming years in Objective 1 Regions (European Commission, 1994a). Another form of intensification is the shrinkage of fallow land, especialiy fal-low for more than one year. Theoretically, the compulsory set-aside of 15% of cropland should cause an increase in the fallow área, but in fact a lot of shrub and pasture land has been ploughed up to maintain the área really under crops. These unproductive plots used to sustain natural vegetation of their own, and played a very important role for 186 birds, especialiy during the reproduction períod as a nesting substratum or for fee-ding chicks (Tellería et al. 1988, Martínez 1992). The declining trend in fallow áreas can be withstood to some degree, although the Spanish govem-ment's application of agroenvironmental measures (R 2078/92/EEC) includes a specifíc progranune to maintain traditio-nal fallow land (MAPA 1994). Fertilizers are being used less in recent years because of their rising príces, and the dosage is much lower than in the more intensified farming áreas of central Europe (Díaz et al. 1994). This is not the case in the more productive steppelands, where fertilizers and biocides are used heavily. In tlie context of farm intensifi-cation, tlie agroenvironmental measures linked to R 2078/92/EEC may become important, and have been extremely use-ful in La Crau (France). Crop fanners in the more cerealist parts of Spain have expressed little enthusiasm^ for the zonal programmes. This lack of acceptance may, hówever, be short-term, and could well change significantly in the coming years. Sheep grazing is essential for the mainte-nance of steppe characteristics (Suárez et al. 1992). Tlie sheep population appears to have remained steady in recent years, although there is a trend towards semi-stabling and overgrazing in some zones. This tendency will probably continué in the coming years. The heavy dependency of farm income on FEOGA-Guarantee subsidies per head (in some zones up to 50% of gross income. Peco & Suárez 1993) m^ üces this sector extremely sensi-tive to future CAP policies. Finally, a bríef comment on structural funds for regional development (LEA-DER Projects). Virtually all of the Iberian steppes lie in Objective 1 regions. Many constitüencies have thus set up LEADER projects, most of tliem focus-sed on local industry or correcting pro-blems of water pollution and solid waste management. These funds can be extre-mely useful for stabilizing the local far-ming population and promoting quality farm products, a sector which may beco-me essential to steppe conservation in the near future. Steppe conservation in EU nature conservation pro-grammes The European Union, via its ACE-Biotopes Programmes and LIFE finan-cial Instruments, has cofunded eight pro-jects aimed at protecting EU steppeland in üie Mediterranean región. Tlie majori-ty have been in Spain (4) and France (3), and onlv one is in Portu<^ al. The main features of these projects are set out in Table 1. Their cost varíes consi-derably from 570,000 to 3,900,000 ECUs), with an average of around 1,535,000 ECUs. They are thus relative-ly costly projects with a 50-75% subsidy, most of which is used to buy or léase land. These sums are distributed very uneven-ly among EU countries. The French pro-jects have received 55% of the total investment in steppe áreas, considerably more than Spain (35%) or Portugal (10%). In comparison with funding for other types of ecosystems in the 1984-1991 períod, steppe projects have only received 7% while wetlands have recei-ved 53% and forests 28% (European Commission 1994b). The majoríty of the projects include rela-tively large land áreas, although they also vary. The central objective of all but one of them is to protect certain bird species or their habitats. The main beneficiaries are NGOs, although occasionally regio-nal and local Govemments parücipate actively. The importance of these pro-jects can be assessed from two perspec-tives: (i) the área affected in comparison with the total área and the áreas protected legally, or (ii) the promotion of the importance of üiese áreas. Legally protected steppes are estimated to cover 50,000 ha in Spain, and none in France, Portugal or Italy (Suárez et al. 1994). Considering that these projects theoretically affect approximately 252,000 ha in Spain, 11,500 ha in France and 2,600 ha in Portugal, we can consi-der the effect to be extremely positive. If these figures are compared with the steppes declared as IB As, however, the área affected by the projects is much poo-rer- around 12% in Spain, 19% in France and 4% in Portugal. Moreover, the Spanish figures may be misieading given that the Los Llanos project in Cáceres is unlikely to reach the specified área. The promotional aspect is difficult to evalúate. Large-scale campaigns by the majority of the NGOs participating in these projects and the construcüon of visitor centres has led to a considerable increase in the number of visitors. This work can thus be considered as positive. Finally, it is essential to consider that pseudosteppe conservation cannot just involve one type of action (Suárez 1994). Although the conservation projects are undoubtedly important, the amount ear-marked for agricultural funds and the áreas of threatened pseudosteppes are several orders of magnitude higher than those for conservation. It is therefore vital to broach the problem from a múl-tiple perspective by combining agricultu-ral, infrastructure and conservation poli-cies to the greatest possible degree. 1 COLLOQUE BIO'MES 1995 ^ Acknowledgemeots ) ^ i Catlierine Levassor gently traiislated Üie abstract into french. References CASTELLANO, E. & Cifuentes, P. 1994. Un problema con repercusiones medioambientales: ¿Explotación agrícola marginal o explotación forestal? Análisis financiero. El Campo, 131: 185-202. DE JUANA, E., Martín-Novella, C, Naveso, M.A., Pain, D. & Sears, J. 1993. Farming and birds in Spain: Threats and opportu-nities for conservation. RSPB Conservation Review, 7: 67-73. DÍAZ, M.C., Garrido, S. & García, R.A. 1994. Contanünación agraria difusa. El Campo, 131: 93-107. European Commission. 1994a. Marco comunitario de apoyo para las regiones objetivo 1 de España. European Comission, Brussels. European Commission. 1994b. Promoting biodiversity in tbe European Community. The ACE-Biotopes Programme 1984-1991. Office for Official Publications of tlie European Communities. Luxembourg. GRIMMET, R.EA. & .Tones, T.A. 1989. Important bird áreas in Europe. ICBPTechnical Publication no 9, Cambridge. GUTIÉRREZ, A., Jiménez, B., Levassor, C, Malo, J.E., Peco, B. & Suárez, F. 1993. Los cambios en el paisaje: enseñanzas para un futuro. Quercus, 88: 14-17 MAÍORAL, R. 1987. La utilización del suelo agricola en España. Aspectos evoluüvos y locacionales. El Campo, 104: 13-26. MANRIQUE, J. & De .luana, E. 1991. Land-use changes and tlie conservation of dry grassland birds in Spain: a case study of Almería province. In PD. Goriup, L.A. Batten & J.A. Norton (eds.), Tlie conser\'ation of lowland dry grassland birds in Europe, pp. 49-58. .Toint Nature Conser\'ation Committee, Peterborough. MAPA. 1994. Programas de ayudas para fomentar métodos de producción agraria compatibles con las exigencias de protección y la conservación del espacio natural. Ministerio de Agricultura, Pesca y Alimentación, Madrid. ¡MARTÍNEZ, C. 1991. Pattems of distribution and habitat selection of a great bustard Otis tarda population in ncMrthwestem Spain. 'Ardeola, 38: 137-147. MIL ARA, R.J. 1995. La fauna en las Evaluaciones de Impacto Ambiental. Doctoral Thesis, ETSIM, Univesidad Politécnica, Madrid (unpublished). MUÑOZ-COBO, J. 1992. Breeding bird communities in tiie olive tree plantations of Southern Spain. Alauda, 60: 108-112. NAVESO, M. A. & Fernández, J. 1993. Propuesta de programa de zona para el área de La Serena en aplicación del reglamento CEE 2078/92. SEO-BirdLife, Madrid (non pubüshed). OÑATE, J..T., Cachón, J., Garcia, F. & Suárez, F. 1995. Los estudios de impacto ambiental de autovias y autopistas en el Estado Español: ¿normativa o interpretación?. Ingenieria Civil, 98: 61-67. PASTOR, M. & Humanes, J. 1991. La reforma de la PAC y el olivar. El Campo, 122: 32-35. PECO, B. & Suárez, F. (coord.). 1993. Recomendaciones para la gestión y conservación del medio natural frente a los cambios relacionados con la Política Agraria Comunitaria (PAC). Universidad Autónoma de Madrid-ICONA, Madrid (non published). SUÁREZ, F. 1994. Mediterranean steppe conservation: a background for the development of a future strategy. Doc. XI/153/94, Euopean Conmiission, Brussels. SUÁREZ, F, Sainz-Ollero, H., Santos, T. & González Bemáldez, F. 1992. Las estepas ibéricas. M.O.P.T., Unidades Temáücas de la Secretaría de Estado para las Políticas del Agua y el Medio Ambiente, Madrid. SUMPSI, .I.M. 1995. Sistemas extensivos en tierras cerealistas. I Curso de Técnicas Agroambieníales, pp. 147-173. Escuela Central de Capacitación Agraria, Ministerio de Agricultura, Pesca y Alimentación, Madrid. TELLERÍA, J.L., Santos, T, Alvarez, G. & Saéz-Royuela, C. 1988. Avifauna de los campos de cereales del interior de España. In F. Bemis (ed.). Aves de los medios urbano y agrícola en las mesetas españolas, pp. 173-317. Monografías de la SEO no 2, SEO, Madrid. Resume Les auteurs analysent les problémes de conservation et les actions comunautaires qui concement les steppes méditerranéennes. La reforestation des ierres agricoles (R. 2080/92/CEE), les plantations d'oliviers et d'amandiers et les grandes infrastructures, subven-üonnées partiellemént p ^ des fonds comunautaires, représentent les changements drastiques qui peuvent concemer de grandes per-ficies. En ouü-e, rintensification des cultures via de nouvelles irrigations et une concentration parcellaire, financées en partie par la FEOGA-orientation, peuvent également avoir d'importantes répercussions. Les actions de conservation entreprises grace á des fonds ACE-Biotopes et LIFE ont permis des actions d'Information et de dynamisation, bien que leurs répercussions en terme de superficies proteges se sont avérées réduites. Les auteurs concluent que la conservation des milieux steppiques doit etre conduite á partir d"une approche múltiple, en essayant de faire coíncider autant que possible les politiques agraires, d'infrastructure et de conservation. 187 ANNEXES r Projecí Steppe bird habitat protection: Tierra de Belchite Habitat conservation: Los Llanos de Cáccres Wetland and arid área conservation: Murcia Houbara bustard habitat conservation: Lanjaies región Natural Reserve creation: TheCrau The Crau séche protection and management, Ist phase The Crau séche protection and management, 2nd phase Steppe bird conservation: Castro Verde plains Years 90-94 91-94 93-95 94-95 88-92 89-93 94-96 93-94 Total budget (ECüsxlO^) 570 1,974 1,806 340 554 1,800 3,900 1,333 Área (ha) 600 245,700 2,598 2,700 150 7,000 11,500 2,600 Bcncfíciary NGO NGO/KG. R.G. R-G. NGO NGO/L.G NGO/L.G. NGO Main Effcct Birds Birds Flora, wet-lands Birds Birds Birds Birds Birds Main actlon Landpurchas Landpwixhas & léase Land piirchas & restoration Landpurchas Management agreements Landpurchas Landpurchas a l ease Landpurchas & léase Table 1 : Projects funded by the E.U. under the ACE-Biotopes and LIFE Programmes which affect Mediterranean steppe zones. NGO : Non-Goveriiment Organlzatlon L,G.: Loca! Government R.G, : Regional Government 188 

Actions and instruments for E.U. steppe habitat conservation

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Actions and instruments for E.U. steppe habitat conservation

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