Five Years of PLEC in Peruvian Amazonia A Final Report on PLEC-Peru Activities: Miguel Pinedo-Vasquez, Pilar Paredes del Aguila, Roberto Romero, Michelle Rios and Mario Pinedo I. Preface: Agrodiversity characterizes smallholder farming in Peruvian Amazonia and the resultant agrobiodiversity and other forms of biological diversity are the main resources upon which poor farmers (known locally as ribereños) depend. Since the mid-1990’s PLEC has been engaged in demonstration activities in villages located in the Sector Muyuy floodplain to identify, test and promote production technologies that are both biodiversity-friendly and economically rewarding. Over the years PLEC-Peru has found that the demonstration methods used by the PLEC project are effective tools for recording agrodiversity and for evaluating agrobiodiversity and other forms of biological diversity that are produced, managed and conserved by ribereños. Through complex agrodiversity practices ribereños use highly dynamic Muyuy environments to produce a great diversity of crops while creating habitats for endangered and overexploited species of fish, river turtles, plants, and wildlife. The ribereño approach of “producing to conserve and conserving to produce” allows them to conserve a great diversity of varieties and species of crops in their fields, house gardens, fallows and forests. In addition, agrodiversity practices help Muyuy’s small farmers to maintain a broad resource base that helps obtain both food and needed cash in difficult times when the Peruvian government agricultural loans and other services were withdrawn. The 1 social and economic values of ribereño agrodiversity are emphasized in this document. The PLEC-Peru team believes that PLEC’s demonstration approach is a critical concept for understanding how biodiversity can be conserved, managed and produced in a sustainable way. We conclude that meaningful attempts at biodiversity conservation must begin at the interface between ecological and social processes and incorporate locally developed knowledge and agrodiversity practices. II. Introduction: This report summarizes the outcomes of integrated research, demonstration and training activities that were implemented over more than five years as part of the global PLEC project. The document provides descriptive and analytical information that explains how PLEC’s demonstration method was implemented in several ribereño communities. Factors that limited or facilitated the recording and dissemination of ribereño agrodiversity practices using the demonstration method are included and discussed in the report. A major objective of the data reported and analyzed in this final report is to demonstrate why it was critical for team members to identify and record agrodiversity practices for understanding how agrobiodiversity and other forms of biological diversity are produced, managed and conserved by small farmers in Amazonia. Results of several studies have shown that important and critical biological resources in Amazonia depend on the agricultural technologies and conservation practices of ribereños. To examine the value of smallholder agrodiversity practices, data were collected on land-cover dynamics using Landsat images, biodiversity inventories and household surveys of resource use technologies and conservation practices were carried out. These were all stored in a 2 database. Following PLEC methodologies, production technologies that are biodiversity friendly and economic rewarding were promoted in demonstration activities. Selected expert farmers were the instructors in each demonstration activity and they used their fields, fallows, house gardens and forests as demonstration sites to conduct field visits and explain how to use the systems and techniques applied. Results from demonstration activities are used to argue why the PLEC approach is valuable for understanding the multi-functionality of agrodiversity in ribereño societies. Most agricultural technologies and conservation practices promoted in demonstration activities were the results of the responses of ribereños to changes produced by ecological and social processes and events in their landscape. Ribereño technologies are clear example of how smallholders deal with the dramatic series of natural and social processes influencing their social and natural landscapes. These technologies are as dynamic as the floodplain environments and the product of continuous interaction with the constant flux in social and physical landscapes. We begin the report by describing the composition and role of the PLEC-Peru team in conducting project activities. Data collected and social processes that shape Muyuy’s landscapes are discussed in the following section. As part of this section we describe the environmental diversity of the Muyuy floodplain. Production technologies and conservation practices recorded in household surveys are reported and discussed in the next section. The agrodiversity data are organized by land forms (levees, silt and sand bars) and land use units (fields, fallows, house gardens and forests). 3 The next section of the report describes and analyzes the agrobiodiversity and other biodiversity data collected and stored in a database during in the last five years. The recorded biodiversity is organized by environment and land use units that composed the landholdings of Muyuy’s residents . Species richness is calculated for fields, fallows, house gardens and forests. This information is compared with the estimated diversity indices of areas that are not under use. The following section is devoted to the description and analysis of the results of demonstration activities. Since the number of demonstration activities and the list of participants for each demonstration activities are included in annual reports, we include here only the average of demonstration activities and participants per year. In this section we also explain how we monitored the assimilation or dissemination of the technologies learned in demonstration activities. The role of expert farmers as instructors in demonstration activities is also analyzed in this section. We argue that ribereños do not copy the technologies but rather modify them and produce new techniques. The final report concludes with a set of recommendations on how to promote ribereño agrodiversity and how to integrate such small farmer technologies into rural development and conservation programs. Recommendations are made based on the results of project activities. Results of demonstration activities are used to recommend methods for training rural extension agents and people working in development and conservation projects. Similarly, we propose specific strategies and methods for making the results of the projects available to wide sectors of the society, particularly to politicians and other groups that are making decisions on development and conservation programs for rural Amazonia. A list of impacts and influences of the project are also 4 included in this section of the report. Since most of the descriptive information on project activities is available separately in a series of reports, in both Spanish and English, this report concentrates on presenting an analysis of project results. III. The PLEC-Peru team: Since the beginning of the project, PLEC-Peru maintained a small interdisciplinary team composed of 3 Peruvian researchers, 3 field assistants, 6 expert farmers and 2 students from the local university (Universidad Nacional de la Amazonia Peruana – UNAP). Although the team managed to train an average of 9 graduate and undergraduate students per year, only 2 of them were incorporated into the team. Three professors from the UNAP and two from the Instituto de Investigaciones de la Amazonia Peruana – IIAP (Research Institute of Peruvian Amazonia) provided technical advice and access to laboratories and libraries. During the five years of the project the team worked in partnership with IIAP and its director was one of the main advisers of the project. In addition, the team maintained a working relationship with leaders of the regional farmers’ union (Federacion de Campesinos y Nativos de Loreto – FEDECANAL). At the outset of the project, relationships were developed with a local non-governmental organization, the Centro del Hombre, Ambiente y Conocimiento de Recursos Amazonicos – CHACRA. The nature and composition of PLEC-Peru team has played a key role in the implementation and monitoring of demonstration activities. Villagers have appreciated the inclusion of expert farmers in the team. With the help of expert farmers the team attracted large participant groups to demonstration activities. The selection and training of field assistants from village also played a key role in advancing the exchange of 5 technologies and germplasm during and after demonstration activities. The participation of local researchers, who have roots in rural communities, also helped in negotiations and the establishment of partnerships with selected expert farmers as well as with local authorities and people working in rural development and conservation programs in the floodplains of Peruvian Amazonia. Although the PLEC-Peru team has few permanent members, other researchers, farmers, leaders and other local experts participated in the processes of design, planning and carrying out demonstration activities. The participation of researchers from Amazonia-based academic and research institutions provided valuable information on the activities of institutions that are working in floodplain villages. Information collected from interviews and reports by members of these institutions helped us identify factors that promote successful demonstration activities and active participation of smallholders. Similarly, the close interaction with village and farmers’ union leaders helped the team develop friendly and trusting relationships with villagers within and outside PLEC sites in Muyuy. IV. The Muyuy floodplain: The total area of the floodplain known as Sector Muyuy is approximately 292 km2 of which approximately 223 km2 is land and 69 km2 is river during the season when river levels are at about an annual midpoint. The Muyuy floodplain is located near Iquitos, the largest urban center in Peruvian Amazonia and ribereños are the largest population group (Fig. 1). Over the last five years the population of Muyuy has experienced slow growth from approximately 3560 in 1995 to 3810 in 2002. Although 8 villages changed their locations due to lateral erosion, the ribereño 6 population of Muyuy remained distributed in 38 villages during the last five years. Muyuy is one of the most densely populated rural floodplain regions in Amazonia with about 67 people per km2. The age and gender composition of the Sector Muyuy population is roughly similar to that of other Amazonian regions (Fig. 2). Muyuy’s population is remarkably young and constantly moving between the villages and the city of Iquitos. Each village family has relatives in the city and the majority of them maintain a house in the shanty towns of the city. The ribereños of Muyuy and neighboring communities are typically engaged in multiple production and management activities. Virtually all of Muyuy’s landscapes are constantly subject to complex and interlinked natural and social processes of change. These processes are highly variable and unpredictable in their frequency, intensity and spatial characteristics. Muyuy is an area dominated by a yearly flood cycle during which river levels rise and fall an average of over 9 meters. When river levels are at their lowest annual level the land area increases by about 30%; when it is at its highest level, virtually all land disappears. Due to its location largely within a highly dynamic floodplain, Muyuy includes a diversity of environments exposed to flooding of varying intensities and frequencies, riverbank erosion and deposition due to lateral migration, as well as other powerful fluvio-dynamic processes. The exact timing and height of floods varies from year to year. The flood regime is not the only agent of change and instability in Muyuy, there are multiple social processes and events that shape the social and natural landscapes. As ribereños interact with natural processes, socioeconomic factors are also constantly altering the availability of resources and the value of what is produced. Political change, including variation in regional, national, and international economic development and 7 credit policies are yet other sources of change and instability that have long affected the biodiversity of Muyuy’s environments. Globalization has long played an important role the lives of Muyuy residents by creating periods of booms and busts that profoundly changed important biological resources of the region (Fig. 3). At the time the project was conducted, the social landscape of the Muyuy floodplain changed drastically due to government changes in rural development and conservation policies. Government services such as agricultural loans, that were available for more than a decade, were abolished by the Peruvian government in the 1990’s. The national agrarian bank (which was the main source of loans for rural people) was closed down, the practice of guaranteeing minimum prices for cash crops such as rice was abolished and the government rural extension agency closed down. In order to endure and prosper in this environment, the Muyuy residents developed technologies and strategies for managing and maintaining high levels of biodiversity, widening the resource base upon which they depend. V. Agrodiversity practiced by the Muyuy’s residents: Ribereño knowledge of diversified resource use and their dependence on a large number of produced, managed and collected resources have enabled them to survive a variety of disasters including the loss of access to agricultural loans, high floods and other political and ecological events. Residents of Muyuy take advantage of fluvio-dynamic and other natural processes to produce, transform, and conserve agrobiodiversity and other forms of biological diversity in their landholdings and surrounding environments. The resultant patchy landscape produced by fluvio-dynamic activities and land use practices provides a great diversity of 8 land, forest and water bodies where they engage in agrodiversity and conservation practices. The diversity of landscape elements such as water bodies, land forms, settlements, forested areas, agriculture fields, fallows and forest gardens produce a great diversity of habitats making the Muyuy one of the floodplain regions with the highest beta diversity () in Amazonia. Such landscape heterogeneity offers farmers many potential agro-environments. Farmers identify and select agro-environments by practicing horizontal and vertical zonation. Based on landscape and land surveys conducted in 1995 and 2001, the four main land forms that compose the Muyuy floodplain offer several environments to ribereños for production of crops (Table 1). High levees and low levees offer more agro-environments than do silt and sand bars (Table 1). While high levees are exposed to only unusually high floods and low levees are inland and not exposed to strong river currents, silt and sand bars are very unstable and affected by both floods and river currents. The relief in each one of the four land forms, however, is characterized by many micro topographic conditions that offer differing micro environmental conditions for the production and management of resources. In addition to relief and other horizontal variations, the landscape of Muyuy presents important vertical variations that facilitate the formation of agro-environments. Different degrees of canopy opening provide a series of light gradients for the growth of shade tolerant and intolerant species. Verticality layering of floodplain vegetation produces agro-environments in the canopy, sub-canopy and suppress layers of the forests (Fig. 4). Vertical zonation of the landscape helps ribereños choose and manage light gradients in agro-environments that are suitable for building agroforestry and agriculture fields. 9 The degree to which agro-environments are used for production and management of resources varies during the aquatic (creciente) and terrestrial (merma) phases. Muyuy is a highly dynamic landscape and the number of agro-environments in each landform is constantly changing. For instance, after floods farmers expect changes in the area and sediments of sand and silt bars and are usually ready to change the species and varieties of crops to be planted. Every year we observed that some areas of sand bars became silt bars or vice versa after floods. Changes in landforms and agro-environments facilitate rather than limit the practices of agrodiversity in the Muyuy floodplain. Data collected in household surveys show that ribereños use a great diversity of production and management technologies for the production, management and conservation of resources (Table 2). Using complex technologies ribereños maintain large numbers of species and varieties of annual as well as habitats for wildlife and fish species (Table 2). For instance, the tablone system (cluster system) allows farmers to plant beans in beaches to create habitat for fish during the flood season. Similarly, the ladera system (edge system) helps farmers reduce damage to corn and other crops by rodents such as capybaras, by planting sugar cane at the margin of fields made in low and high levees. On the relatively stable levees farmers practice more production and management systems and techniques than on the unstable silt and sand bars. The combination of production and management practices we refer to as agrodiversity, allows farmers to build and maintain different kinds, sizes and ages of fields, fallows, house gardens and forests (Table 3). For instance, each household that we surveyed maintains a field or fallow for trapping rodents and land birds. Similarly, the 10 integrated management and conservation of forested areas provide valuable resources to ribereños. Managing forest for multiple uses including for fishing explain why ribereños maintain more different kind of forest in low rather than in high levees. In contrast, more kinds of fallows are managed in high than in low levees, because farmers need the areas for making fields or planting agroforestry crops that are less resistant to floods. Ribereños also make more kinds of house gardens in high than low levee areas. The two kinds of house gardens managed by farmers in low levees produce habitats for fish that help farmers to catch fish during the flood season. The multi-functionality of farmer’s technologies has help to conserve biodiversity in the Muyuy dynamic floodplain. VI. Biodiversity in the landholdings of ribereños: Ribereño practices of diverse land and resource use systems help them to maintain high levels of biodiversity in the dynamic Muyuy floodplain. Their landholdings contain an immense diversity of species, ecosystems, landscapes and environments. Farmers’ maintenance of large numbers of species and varieties of crops allows them to keep farming on the four main landforms of the Muyuy floodplain (Fig. 5). Riberenños plant varieties of beans, rice, watermelon and other annual crops that are particularly adapted to the flood pulse. Some of the varieties locally known as dos mesinos (“two months”) are planted on the lowest parts of silt and sand bars. Most varieties of annual crops planted on silt and sand bars can also withstand floods and remain under water for at least two weeks. Farmers explain that the capacity of crops to remain alive under water attracts fish and river turtles that make easy to fish while farming. 11 The general pattern observed in Muyuy and reflected in the biodiversity inventory data is that smallholders tend to maintain or in same cases increase levels of biodiversity in all land use stages. Plant species that produce valuable “forest products” are planted and incorporated in their fields, fallows, forests and house gardens. It is common to find seedlings of timber and forest fruit species growing in fields. The range of Shannon Index values (H’= 0.91 to 1.87) clearly show that ribereños maintain biodiversity-rich fields in the very dynamic Muyuy floodplain (Table 4). In most cases ribereños have purposely planted a lesser number of crops in their fields in order to encourage the natural regeneration of valuable shrubs and tree species. Such strategies explain why it is common to find fallow areas in their landholdings where the density of juveniles of timber and other valuable tree species is very high. Management of fallows for multiple uses (including for providing habitats for rodents, land birds and even fish) help ribereños to obtain many products for their consumption and the market. Data collected in household and land surveys show that each households maintain fallow areas under different intensities of management (Table 5). Differences in the range of Shannon Index values (H’= 1.79 to 3.68) among fallows clearly demonstrate that biodiversity levels vary considerably with the intensity and frequency of the owners’ interventions (Table. 5). Farmers who were interviewed corroborated the estimated Shannon Index values, by mentioning that vegetation in fallows where no management operations were conducted tend to be dominated by individuals of cetico (Cecropia membraneaceae). Ribereños have managed to control the establishment and dominance of cetico, by managing individuals of valuable species in a spatial arrangement that allows them to compete with fast growing species. The 12 application of such management strategies varies not only among households but also among villages (Figure 6). We found that farmers in some villages maintain more biodiverse fallows than do those in other villages (Figure 6). These villages are locally known to be purmeros (“fallow users”) due to the amount of fallow products that they consume and sell in the markets. The majority of forest areas that are part of the landholdings of ribereños are the results of successive management operations that began at the field stage and continued into the fallow and forest stages. Inventories conducted in a sample of 9 plots of multipleage managed forest (each 900m2 in size) show that the forests in ribereño landholdings contain high levels of species richness. The mean average number of plant species per hectare estimated using data collected in the 9 plots is greater (83) than the number (52) found in forests that were not reported as managed. The range of variation in the Shannon index (H’= 1.77 to 3.98) is similar in pattern to that estimated for managed fallows. We found that the differences in species richness and Shannon index values among forests reflect the histories of management and resource extraction practiced by their owners. Field observation and interviews suggest that some ribereños are more dedicated to enriching their forest with timber species, while others are more interested in fruit and medicinal species. Despite the abundance of commercially valuable plant species, inventory data show that ribereños also maintain small numbers of individuals of some non-commercial species. Among these are pioneer species such as Cecropia membraneaceae that play an important role in attracting game animals and fish during floods. Ribereños keep constantly removing individuals of Cecropia and other fast growing species to make light available for the regeneration of more valuable species. By 13 removing adult individuals and encouraging the establishment and growth of seedlings and juveniles, farmers maintain forests where the density of individuals is correlated with the number of species (Figure 6). House gardens are also very important reservoirs of biodiversity for Muyuy farmers. We found that farmers have many species and varieties of herbs, vines, shrubs, grasses and trees in their house gardens. There is more variation in number of individuals and species planted in house gardens than in fallows and forests (Figure 8). Variations in species and density of individuals reflects different uses of house gardens. While some house gardens are used more for ornamentation and shade, others serve as nurseries and for experimenting with the cultivation of forest or exotic species. In most cases house gardens provide fruits, species, medicinal plants and other resources for the consumption and the market. The kind of uses and the intensity of management reflects variation in species richness among house gardens (Table 7). Results of the biodiversity surveys presented and discussed above show that a great diversity of resources are produced, managed and protected by ribereños in their landholdings. The reported levels of agrobiodiversity and other forms of biodiversity should add useful biological data and further clarify the complex and diverse operations and technologies used by smallholders to produce and maintain Amazonian biodiversity in a highly dynamic environment such as the Muyuy floodplain. VII. Demonstration activities: In most of Peruvian Amazonia government agencies play at most a very marginal role in rural development and conservation programs. Existing development and conservation programs in Muyuy as in much of rural Amazonia, are conducted by non-governmental agencies. Although PLEC-Peru did 14 not function as an NGO, the residents of Muyuy at first perceived the team as belonging to an NGO and PLEC demonstration activities as yet another standard NGOimplemented program. Despite our explaining that PLEC activities differed substantively from other “training courses”, most farmers (particularly the leaders) did not initially distinguish our efforts from training courses that NG0’s offer and that are frequent in Muyuy and neighbouring regions. After speaking with farmers about demonstration activities and how we were interested in promoting ribereño-developed production and management techniques we found that the majority of wanted to see results before they decided to incorporate any demonstrated techniques in their repertoires. PLEC-Peru involved expert farmers (who were identified and selected in household surveys) in designing, planning and the implementation of demonstration activities. Expert farmers demonstrated their production and management techniques and used their fields as demonstration sites to show the results of such employing their carefully developed techniques. Gradually most farmers discovered that PLEC demonstration activities were different from the training courses given by NGOs. They found that demonstration activities do not lack concrete examples of the results obtained by using the demonstrated techniques. PLEC-Peru did not use experimental and training centres as demonstration sites, but rather the fields, house gardens, fallows and forests of expert and successful farmers. Through observation and discussions with many farmers, we found that most Amazonian farmers value training courses as opportunities to socialise rather than to learn production systems and techniques. Based on this information, PLEC-Peru has promoted formal demonstration activities as part of village or inter-village meetings 15 (reuniones) and did incorporate some social activities into the meetings. Expert farmers told the team that most farmers are learn new techniques while working in mingas and by participating in visitas a la familia. Mingas are shared labour groups organised by members of households to help each other with agricultural activities. Visitas, are typically gatherings of families or close friends. PLEC-Peru incorporated these forms into a diversity of demonstration activities. In both more and less formal meetings, expert farmers are the leading figures and are the ones who invite participants to visit demonstration sites. For the Peruvian team, demonstration activities provided an opportunity for identifying and critically analysing the processes and methods by which production and management technologies are transferred and shared among ribereño farmers. PLECPeru’s demonstration activities are conducted following several models in each of which selected expert farmers act as instructors, and their fields, fallows, house gardens and forests are used as demonstration sites. Although our results are still preliminary, we believe they indicate the success of giving the role of instructor to local farmers. Over the last five years of activities a number of important lessons were learned while conducting demonstration activities. The integration of expert farmers into all phases of demonstration activities helped the Peruvian team to identify several specific approaches. During the first year of the project the team planned and conducted demonstration activities as part of reuniones. The other three years the team was engaged in organizing mingas and visitas following the advice of the expert farmers. During the five years we held an average of 12 reuniones, 60 mingas and 25 visitas per year (Table 7). The largest number of participants were 16 involved in mingas and the smallest in visitas. The increased participation of farmers in mingas is now greatly helping expert farmers to promote biodiversity friendly and economic rewarding resource use systems within and outside the Muyuy floodplain. Although PLEC-Peru identified a large number of successful production and management systems and techniques (see table 2), only few of these have been promoted in demonstration activities (Table 8). The main reason why the majority of systems and techniques are not promoted is because the expert farmers who are using them are still not willing to demonstrate them as part of PLEC activities. Expert farmers who are integrated into the team are demonstrating 9 systems for producing and managing resources in higher levees (Table 8); they are promoting 4 systems for planting crops on low levees, 3 systems to cultivate annual crops on sand bars and 2 systems for planting rice and other crops on silt bars (Table 8). Most farmers who participated in demonstration activities have begun testing the techniques that they learned from the expert farmers and observed in demonstration sites. The team learned that smallholders do not copy the production and management techniques demonstrated by the expert farmers. Instead they combine these ideas with their own and create new and original techniques. Farmers tend to incorporate the learned production and management technologies only after a long process of experimentation. We found that the trial and error approach employed by farmers to test technologies and crops is increasing the diversity of technologies used through the modification of demonstrated techniques and systems. The diversity of responses from participant farmers allowed PLEC-Peru team to make changes in the structure and direction of demonstration activities. For instance, 17 excessive formality in establishing partnerships with expert farmers limited the success of demonstration activities at the beginning. The team has learned that exchange of knowledge and experiences among farmers takes place in an informal environment. However, such informality makes it difficult to record and monitor the flow of production and management technologies and conservation initiatives thought by expert farmers in demonstration activities. PLEC-Peru has dealt with this problem by 1) maintaining a team composed of members with a strong rural background and experience working with ribereños; 2) having most members of the team spend their time in the field, conducting field observations, following farmers in their daily activities, engaging in informal conversations with farmers and writing daily observations; and 3) building a data base for each household whose members participated in demonstration activities. While the three strategies used by the team are helping us document the expert farmer to farmer exchange, recording the flow of knowledge in an informal environment is still the most difficult and complex problem that PLEC-Peru is facing in the application of PLEC demonstration methods. VIII. Conclusions and Recommendations: The Muyuy case shows that ribereños do not separate conservation from production as is done by experts engaged in the promotion of conventional development and conservation programs. The dynamic nature of the floodplain with high local turnover of habitats and species creates ecological conditions for practicing resource use systems where conservation and production practices are united. Residents of Muyuy “produce to conserve and conserve to produce” as part of a long tradition of making their livelihoods in a rich but highly risky 18 environment characterized by extreme natural and social dynamism. Agrodiversity has allowed ribereños to profit economically while enhancing the conservation of floodplain biodiversity. Ribereño production, management system and conservation practices are valuable technological resources that can help to reduce the current rates of biodiversity loss while enhancing income sources for the rural poor. We offer the following recommendations for promoting and integrating such small farmer technologies into rural development and conservation programs: 1) The transfer of technologies in ribereño societies is done mainly through existing formal (meetings and festivities) and informal (labor groups, family and neighbor’s gatherings) channels rather than through training courses and other urban forms. PLEC’s demonstration approach provides the tools for using such existing forms of farmer interaction. Therefore, we recommend that such demonstration activities be more frequently employed in rural development programs. Demonstration activities should use existing forms of social gatherings 2) The promotion of farmer’s technologies is greatly facilitated when is conducted by farmers. We recommend the inclusion of expert farmers as team members of rural extension programs dedicated to train farmers. It is important to identify and select the right individuals to do this training. We found that in rural communities, the leaders or more outspoken members are often less qualified to promote successful and innovative farmer technologies. However, there are individuals that are well known by other members of the communities as good farmers with 19 particular techniques for the production, management and conservation of resources. These individuals we recognized as expert farmers. 3) We recommend the use of expert farmers’ fields, fallows, forests and house gardens as demonstration sites. Ribereños are generally very pragmatic, therefore they like to see results and not to hear about the results of particular production system or technique tested under unfamiliar conditions. In addition, farmers tend to value more the technology that is promoted when they see how successful the expert farmer is. 4) In Peruvian Amazonia, there are many programs for inventorying biodiversity and uses of biodiversity. We recommend that as part of these programs, some efforts should go to inventories of production and management systems as well as conservation initiatives used by farmers. 5) The integration of farmer technologies and conservation initiatives in development and conservation programs should clarify how they aim to satisfy farmers’ agendas and not merely the priorities of outside institutions. In many cases in Muyuy farmers have refused to participate in demonstration activities when it was not clear how they would benefit. PLEC-Peru also would like to recommend the following strategies and methods for promoting the results of demonstration activities in a wide social context. 1) We help rural community leaders to summarize the results of demonstration activities and present to government officials. Such documents are discussed with government representatives and new demonstration activities are promoted. 20 2) Members of the team organize demonstration activities for politicians, people working in development and conservation that include visits to demonstration sites and demonstration sessions with expert farmers. 3) A set of manuals, posters and pamphlets that illustrate the production technologies and conservation practices that are promoted in demonstration activities are been produced by the team. 4) Members of PLEC-Peru are also advising the government on the design of new rural development and conservation policies. While ribereños were the main target group in PLEC-Peru work, there are important impacts of the project on the way politicians, researchers and students think about rural development and conservation. PLEC-Peru is managing to have important influence not only on people working for the government but also on people working for NGOs. We would like to mention some of the most relevant impacts of the results of PLEC-Peru work. There has been interest expressed by local university officials in introducing PLEC ideas into a new curriculum for training agronomists, biologists, foresters and sociologists. This development indicates a substantive change of view among university officials. All of the approximately 34 students that were trained and advised by PLEC-Peru have graduated and are currently working in key positions in NGOs and government institutions. They are facilitating the incorporation of PLEC methodology and thus changing the rural development and conservation programs of NGOs and government agencies. The demonstration sites of PLEC-Peru and our experienced expert farmers have been used by NGOs and government conservation 21 officials (INRENA) as examples of sustainable use of biodiversity. Two of the most influential elected local politicians are helping us frame a proposal for implementing demonstration activities as part of rural extension. 22 Figures & Tables Fig. 2: Percent of the population of Muyuy according to sex and age in 2002 75 + 70 - 74 65 - 69 60 - 64 55 - 59 50 - 54 45 - 49 40 - 44 35 - 39 30 - 34 25 - 29 20 - 24 15 - 19 10 - 14 5-9 0-4 female male 20 15 10 5 0 Percent by sex 23 5 10 15 20 Figure 3: A timeline of economic booms and busts that influenced the population and natural resources in Muyuy A rise and collapse of fundos (small latifundios) from 1940s to 1950s In the 1950s and 1960s there was a timber boom to supply the international demand for high grade wood A firewood boom for fueling steam boats at the end of the 19th and beginning of the 20th century In the 1970s there was a short boom produced by oil exploration A turtle egg boom to supply the demand for olive oil during World War II Agricultural loans in the 1980s 1900 2000 1920 1940 24 1960 1980 Fig. 4: Vertical zonation in a patchy landholding in Muyuy, Peru Canopy (trees & vines) Sub-canopy (Shrubs and vines) Suppress (herbaceous & natural regeneration) 25 Fig 5. Horizontal zonation and number of species and varieties planted in each landform high river level low river level High levee 112 species 274 varieties Low levee 72 species 188 varieties Silt bar Sand bar 28 species 96 varities 26 17 species 62 varieties river Figure 6: Range of fallow diversity in Muyuy 27 Figure 7. Comparison of species richness and number of individuals in a sampled of 10 sampled managed forests (average area 0.9 ha). All trees greater than or equal to 5cm dbh were inventoried 28 Figure 8. Comparison of Area and Species Richness for 13 sampled house gardens 29 Table 1: Agro-environments used by ribereños in the four main land-forms of the Muyuy floodplain. Three land-surveys were conducted Average number were estimated using data collected in three land surveys (1995, 1999 and 2001) in the 38 villages Land Forms Average Number of Agro-environments High levee 34 Low levee 17 Sand bar 7 Silt bar 3 Table 2: Average number of production and management systems and techniques used by ribereños to farm in high levees, low levees, silt and sand bars. Land-forms Systems Techniques High levees 32 53 Low levees 17 36 Sand bars 8 18 Silt bars 5 12 Table 3: Average number of kinds of fields, fallows, house gardens and forests maintained by ribereños in their landholdings Land use unites High levees Low levees Sand bars Silt bars Fields 9 5 3 2 Fallows 18 13 1 1 House gardens 4 2 0 0 forests 7 11 0 0 30 Table 4: Variation on species richness and Shannon Index among fields made in levees by 11 sampled households (Average size of each field was 0.5 ha). Villages 1 2 3 4 5 6 7 8 9 10 11 land use stage field field field field field field field field field field field Area Number of Species Shannon Sampled Individuals Richness Index 175 323 8 1.10 849 7104 13 1.10 162 115 8 0.91 3535 606 13 1.87 192 236 8 1.26 612 773 7 1.06 207 357 9 1.62 354 835 11 1.73 1848 166 10 1.33 800 1364 12 1.66 319 180 12 1.29 Table 5: Species richness and estimated Shannon index for a sampled of 6 managed fallows Villages 1 2 3 4 5 6 Area Sampled Individuals Species Richness 900 114 25 900 363 38 342 55 10 900 259 36 900 369 72 900 158 22 31 Shannon 2.80 2.35 1.99 2.45 3.68 1.79 Table 6: Species richness and estimated Shannon index in 9 samples of managed forests Villages 1 2 3 4 5 6 7 8 9 Area Sampled Individuals Species Richness 900 501 81 900 182 82 900 258 74 900 252 96 900 402 74 900 352 82 900 417 88 900 361 93 900 272 78 Shannon 2.50 2.43 3.60 3.09 1.77 3.71 3.98 2.48 1.29 Table 7. Species richness and estimated Shannon Index in 14 sampled house gardens Villages 1 2 3 4 5 6 7 8 9 10 11 12 13 14 land use Area Sampled Individuals Species stage Richness house garden 9928 401 25 house garden 1176 1584 62 house garden 8000 568 29 house garden 1800 135 27 house garden 8000 765 39 house garden 2000 259 22 house garden 1500 303 33 house garden 1539 109 26 house garden 4000 480 21 house garden 6000 161 17 house garden 9000 210 29 house garden 5000 696 22 house garden 10000 353 25 house garden 4000 337 53 32 Shannon 2.15 3.19 2.44 2.88 2.03 2.40 2.25 2.24 1.86 2.31 2.37 2.01 1.75 3.24 Table 8: Average number of demonstration activities carried out by the PLEC-Peru team from 1995 to February 2002. The average number of participants in each and all activities during the year are also included. Demonstration Average Activities Average Average Activities per year Participants Participants per year Reuniones 12 360 30 Mingas 60 1140 19 Visitas 25 225 9 33 Table 9: Number of production and management systems demonstrated by expert farmers in demonstration sessions and visits to demonstration sites during the last five years. List of systems Description High levees: 5) Vuelito Production of vegetables, spices and medicinal herbs under shade 6) Bajada Management trees and vines that are tolerant to high humidity 7) Ladera Production of annual or semiannual crops at the edge of fields 8) Shunto Production of spices and vegetables using ashes 9) Quiruma Production of medicinal herbs and spices around tree stems 10) Retama Production of beans, corn and banana using leguminous trees 11) Estacas A system to produce beans using poles of a Ginerium species 12) Ensombrado A system to produce annual and semiannual crops under trees 13) Huactapeo A system for the management of seedlings of trees in fields and fallows Low levees: 1) Encañdo A system for controlling rain water in fields 2) Enposado A system that help to maintain high humidity for rice production 3) Enpurmado A system of leaving weeds to control infestation of insects on corn 4) Sogal A system for managing selected vines in fallows and forests Sand bars: 1) Tablone A system for planting beans, peanuts and water melon in blocks 2) Hilera A system for planting water melon at the edge of sand bars 3) Tacarpeo A system for planting cassava with squash in the highest part of sand bars Silt bars 1) Voleo A system for planting pre-germinated rice in the lowest part of silt bars 2) Regado A system for planting rice in the highest part of silt bars 34