1 Biodiversity, Agriculture, and Ecosystem Services D.I. JARVIS, C. PADOCH, AND H. D. COOPER
Biodiversity in agricultural ecosystems provides our food and the means to produce it. The variety of plants and animals that constitute the food we eat are obvious parts of agricultural biodiversity. Less visibleâbut equally importantâare the myriad of soil organisms, pollinators, and natural enemies of pests and diseases that provide essential regulating services that support agricultural production. Every day, farmers are managing these and other aspects of biological diversity in agricultural ecosystems in order to produce food and other products and to sustain their livelihoods. Biodiversity in agricultural ecosystems also contributes to generating other ecosystem services such as watershed protection and carbon sequestration. Besides having this functional significance, maintenance of biodiversity in agricultural ecosystems may be considered important in its own right. Indeed, the extent of agriculture is now so large, any strategy for biodiversity conservation must address biodiversity in these largely anthropogenic systems. Moreover, biodiversity in agricultural landscapes has powerful cultural significance, partly because of the interplay with historic landscapes associated with agriculture, and partly because many people come into contact with wild biodiversity in and around farmland.
This book examines these various aspects of agricultural biodiversity. A number of chapters examine crop genetic resources (chapters 1, 2, 3, 10, 11, and 16) and livestock genetic resources (chapters 4, 5, and 17). Other chapters examine aquatic biodiversity (chapter 6), pollinator diversity (chapter 7), and soil biodiversity (chapter 8). Three chapters (9, 10, and 11) examine various aspects of the relationship between diversity and the management of pests and diseases. Chapters 12 and 13 explore farmer management of diversity in the wider context of spatial complexity and environmental and economic change. Chapter 14 looks at the contribution of diversity to diet, nutrition, and human health. Chapters 15 through 17 explore the value of genetic resources and of the ecosystem services provided by biodiversity in agricultural ecosystems.
This introductory chapter sets the scene for the subsequent chapters. After reviewing recent efforts to address agricultural biodiversity in the academic community and international policy fora, the multiple dimensions of biodiversity in agricultural ecosystems are surveyed. Subsequent sections examine the value of ecosystems services provided by biodiversity, the functions of biodiversity, and how these are influenced by management. The chapter concludes with a brief consideration of the future of biodiversity in agricultural ecosystems.
Recent and Current Initiatives to Address Agricultural Biodiversity
The importance to agriculture of crop, livestock, and aquatic genetic resources has long been recognized, but only in the last decade or so has the global community acknowledged the significance of the full range of agricultural biodiversity in the functioning of agricultural ecosystems. In the international policy arena, agricultural biodiversity was addressed for the first time in a comprehensive manner by the Conference of the Parties of the Convention on Biological Diversity (CBD) in 1996. The CBD program of work on agricultural biodiversity, which was subsequently developed and adopted in 2000, recognizes the multiple dimensions of agricultural biodiversity and the range of goods and services provided. In adopting the program of work, the Conference of the Parties recognized the contribution of farmers and indigenous and local communities to the conservation and sustainable use of agricultural biodiversity and the importance of agricultural biodiversity to their livelihoods. Within the framework of the conventionâs program of work on agricultural biodiversity, specific initiatives on pollinators, soil biodiversity, and biodiversity for food and nutrition have been launched.
This new spotlight on agricultural biodiversity is a response to a broad consensus that global rates of agricultural biodiversity loss are increasing. Estimates from the World Watch List of Domestic Animal Diversity note that 35% of mammalian breeds and 63% of avian breeds are at risk of extinction and that one breed is lost every week. The State of the Worldâs Plant Genetic Resources for Food and Agriculture (PGRFA) describes as âsubstantialâ the loss in diversity of plant genetic resources for food and agriculture, including the disappearance of species, plant varieties, and gene complexes (FAO 1998). Every continent except Antarctica has reports of pollinator declines in at least one region or country. Numbers of honeybee colonies have plummeted in Europe and North America, and the related Himalayan cliff bee (Apis laboriosa) has experienced significant declines (Ingram et al. 1996). Other pollinator taxa are also the focus of monitoring concerns, with strong evidence of declines in mammalian and bird pollinators. Globally, at least 45 species of bats, 36 species of nonflying mammals, 26 species of hummingbirds, 7 species of sunbirds, and 70 species of passerine birds are considered threatened or extinct (Kearns et al. 1998).
The broad consensus on amplified rates of biodiversity loss in agricultural systems, with the need to have better quantification of these rates of change, has spurred an increasing number of international, national, and local actions on agricultural biodiversity management over the last few years. The International Plant Genetic Resources Institute (IPGRI) global on-farm conservation project (Jarvis and Hodgkin 2000; Jarvis et al. 2000); the People, Land Management and Environmental Change (PLEC) Project (Brookfield 2001; Brookfield et al. 2002); the Community Biodiversity Development and Conservation (CBDC) Programme; the Centro Internacional de Agricultura Tropical (CIAT), Tropical Soil Biology and Fertility Institute (TSBF), and Global Environmental Facility Below Ground Biodiversity (BGBD) Project; the Global Pollinator Project supported by FAO; and Operational Programme on Agricultural Biodiversity and projects supported under the Global Environment Facility (GEF) are a few prominent examples. Many case studies carried out under these and other initiatives were reviewed at the international symposium âManaging Biodiversity in Agricultural Ecosystems,â held in 2001 in Montreal on the margins of the meeting of the Scientific Subsidiary Body to the CBD.
This book builds on case studies presented at the Montreal symposium. Whereas conventional approaches to agricultural biodiversity focus on its components as static things, many of the chapters in this book emphasize instead the dynamic aspects of agricultural biodiversity and the interactions between its components. Researchers with back-grounds and interests in the social and environmental sciences have also brought new perspectives and approaches to the field. They seek to understand the processes and linkages, the dynamism and practices that are essential to the way biodiversity has long been and continues to be managed in farming systems, agricultural communities, and the broader societies.
Multiple Dimensions of Agricultural Biodiversity
Agricultural biodiversity includes all components of biological diversity relevant to the production of goods in agricultural systems: the variety and variability of plants, animals, and microorganisms at genetic, species, and ecosystem levels that are necessary to sustain key functions, structures, and processes in the agroecosystem. Thus it includes crops, trees, and other associated plants, fish and livestock, and interacting species of pollinators, symbionts, pests, parasites, predators, and competitors.
Cultivated systems contain planned biodiversity, that is, the diversity of plants sown as crops and animals raised as livestock. Together with crop wild relatives, this diversity comprises the genetic resources of food agriculture. However, agricultural biodiversity is a broader term that also encompasses the associated biodiversity that supports agricultural production through nutrient cycling, pest control, and pollination (Wood and Lenne 1999) and through multiple products. Biodiversity that provides broader ecosystem services such as watershed protection may also be considered part of agricultural biodiversity (Aarnink et al. 1999; CBD 2000; Cromwell et al. 2001).
This volume takes a broad and inclusive approach and attempts to point to emerging issues in research on biodiversity in agricultural ecosystems. Chapters 2 to 7 focus primarily on diversity among crops, livestock, and fish that constitute much of the planned biodiversity in agricultural systems. In addition to domesticated crops and livestock, managed and wild biodiversity provides a diverse range of useful plant and animal species, including leafy vegetables, fruits and nuts, fungi, wild game insects and other arthropods, and fish (including mollusks and crustaceans as well as finfish) (Pimbert 1999; Koziell and Saunders 2001; also see Halwart and Bartley, chapter 7). These sources of food remain particularly important for the poor and landless (Ahkter in box 13.2, chapter 13) and are especially important during times of famine and insecurity or conflict where normal food supplies are disrupted and local or displaced populations have limited access to other forms of nutrition (Scoones et al. 1992; Johns, chapter 15). Even at normal times such associated biodiversityâincluding âweedsââoften is important in complementing staple foods to provide a balanced diet. Some indigenous and traditional communities use 200 or more species for food (Kuhnlein et al. 2001; Johns and Sthapit 2004; Johns, chapter 15).
Diversity at species and genetic levels comprises the total variation present in a population or species in any given location. Genetic diversity can be manifested in different phenotypes and their different uses. It can be characterized by three different facets: the number of different entities (e.g., the number of varieties used per crop and the number of alleles at a given locus), the evenness of the distribution of these entities, and the extent of the difference between the entities. Crop genetic diversity can be measured at varying scales as well (from countries or large agroecosystems to local communities, farms, and plots), and indicators of genetic diversity are scale dependent. These issues are examined for crops by Brown and Hodgkin (chapter 2) and Sadiki et al. (chapter 3), for livestock by Gibson et al. (chapter 5), and for aquatic diversity in rice ecosystems by Halwart and Bartley (chapter 7). These chapters are complemented by case studies that illustrate how farmers name and manage units of diversity in their agricultural systems for crops (Sadiki et al., chapter 3; Hodgkin et al., chapter 4), animals (Hoffmann, chapter 6), and aquatic resources (Halwart and Bartley, chapter 7).
Chapters 8 to 10 focus on the essential role of associated biodiversity in supporting crop production (see also Swift et al. 1996; Pimbert 1999; Cromwell et al. 2001). Earthworms and other soil fauna and microorganisms, together with the roots of plants and trees, maintain soil structure and ensure nutrient cycling (Brown et al., chapter 9). Pests and diseases are kept in check by parasites, predators, and disease-control organisms and by genetic resistances in crop plants themselves (Wilby and Thomas, chapter 10; Jarvis et al., chapter 11; Zhu et al., chapter 12), and insect pollinators contribute to the cross-fertilization of outcrossing crop plants (Kevan and Wojcik, chapter 8). It is not only the organisms that directly provide services supporting agricultural production but also other components of food webs, such as alternative forage plants for pollinators (including those in small patches of uncultivated lands within agricultural landscapes) and alternative prey for natural enemies of agricultural pests. This has been shown in Javanese rice fields, where complex food webs ensure that the natural enemies of crop pests such as insects, spiders, and other arthropods have alternative food sources when pest populations are low, providing stability to this natural pest management system (Settle et al. 1996).
The multiple dimensions of biodiversity in cultivated systems make it difficult to categorize production systems as a whole into high or low biodiversity, especially when spatial and temporal scales are also included. In chapter 11, Jarvis et al. discuss whether crop genetic diversity is a benefit in reducing disease in time or whether it could be a hazard, given the potential emergence of pathogen super-races. They present case studies of resistant local genotypes used by farmers, use of resistance in intra-specific variety mixtures, and breeding programs that have selected for and used genotypes resistant to pests and pathogens to reduce crop vulnerability. The authors note the challenge of developing criteria that determine when and where genetic diversity can play or is playing a role in managing pest and disease.
Although academic research on agricultural biodiversity typically has focused on specific components...