Successful Agroforestry Research Articles

Spreading Agroforestry for Sustainability: A Comparative View of Shandong and Sichuan Provinces

Abstract Facing severe ecological damages and a large population, it is imperative for farmers of the Sichuan Province to seek alternative land-use practices to optimize their production. Agroforestry, the union of agriculture, forestry, and/or livestock in one harmonious system, is one way verified to increase agricultural productivity and to boost the environmental state of wellbeing. This study examines the incentives and initiatives supporting the successful agroforestry systems in Shandong and evaluates whether such an experience would be successful in Sichuan as well.

Competition for light between hedgerows and maize in an alley cropping system in Hawaii, USA

Successful agroforestry systems depend on minimizing tree-cropcompetition. In this study, field experiments and a simulation model were usedto distinguish between tree-crop competition for light and belowgroundcompetition in an alley cropping system. Maize (Zea maysL.) was harvested periodically in three treatments: between vertical barriers ofshade cloth, hedgerows of Flemingia macrophylla (Willd.)Merr., and sole maize. Radiation intercepted by the maize was calculated using asimulation model based on measured values for direct and diffuse light, hedgerowdimensions and leaf area, and solar trajectory. Radiation use efficiency wascalculated as biomass production per unit of intercepted radiation. Maizebiomass and yield in both the alley crop and the shade cloth treatment weregreatest in the center of the alleys. Grain yield between hedgerows was 3.5Mg ha−1 (averaged across the alley), significantlyless than in the shade cloth (7.4 Mg ha−1) or thesole maize (7.7 Mg ha−1) treatments. Lightintercepted by the maize in the alley crop was about half that intercepted bythe maize in the sole crop. The shade cloth intercepted less light than thehedgerows because it did not have an appreciable width. Radiation use efficiencyin the three treatments was 0.75 g mol−1 PAR anddid not differ significantly among treatments. Tree-crop competition wasoverwhelmingly for light.

Adopting Agroforestry

This study was conducted in rural central and northern Malawi to (1) identify factors limiting/enhancing agroforestry adoption and (2) assess the impact of cultural differences on the adoption and use of agroforestry systems. The study involved interviewing representatives of a large number households concentrated in four separate study areas. The study used the grounded theory method of sociology, which relies on largely qualitative data and inductive reasoning. Nine-tenths of the farmers in the study were resource poor with little or no formal education. Two-thirds of the farmers in the study were not familiar with agroforestry systems such as alley cropping. The level of interest in adopting agroforestry systems, which did not include the application of inorganic fertilizer, was quite high because of anticipated improved crop yields. An overriding theme emerging from the study was the importance of considering micro-level economic conditions and cultural dynamics in the design of successful agroforestry programs. The results also suggest the utility of local level social analysis prior to efforts designed to further promote the adoption of agroforestry. Clearly, biological sus-tainability is essential, but not sufficient in the design of such programs.

Agroforestry performance on small farms in Amazonia : Findings from the Rondonia Agroforestry Pilot Project

Experiences from not only ‘success stories’ but also ‘failed’ agroforestry projects provide potentially useful lessons for future agroforestry-project designers. Experimental one-hectare agroforestry plots were established on 50 small-scale farms in the western Brazilian Amazon State of Rondonia from 1993 to 1995. Drawing from a menu of 25 different species (10 tropical hardwoods and softwoods and 15 fruits and palms), this species trial shows encouraging survival and growth performance for most species under wide ranging plot management regimes. Tropical hardwood survival rates (after 18 months) ranged from 65% for Cerejeira (Torresea acreana) to 88% for mahogany (Swietenia macrophylla). Survival rates for commercial fruit and palm species were even higher. A comparison of attributes of two sub-groups (successful and unsuccessful planters) suggests that previous experience with perennial monocultural cropping, greater social participation, land use history, and soil chemistry are positively associated with successful agroforestry species performance, while no significant differences exist between successful and unsuccessful planters in household size, area deforested, area in pasture, and land tenure security. A closer analysis of ‘failed’ agroforestry plots indicates the primary importance of social factors originating at the household-level (e.g. inadequate plot maintenance, improper planting techniques, illness, etc.). Twelve different causes of plot failure were cited, falling into three classes. Of the total number of reasons given for plot failure, household level factors represented 54% of all causes cited. Project design and implementation factors (inappropriate plot design, defective planting material, etc.) were cited 25% of the times and environmental factors (soil fertility constraints and pasture grass invasion) were cited 21% of the times.

Transpiration rates and canopy conductance of Pinus radiata growing with different pasture understories in agroforestry systems.

We measured tree transpiration and canopy conductance in Pinus radiata D. Don at two low rainfall sites of differing soil fertility in Canterbury, New Zealand. At the more fertile Lincoln site, we also assessed the effects of two common pasture grasses on tree transpiration and canopy conductance. At the less fertile Eyrewell Forest site, the effect of no understory, and the effects of irrigation in combination with mixtures of grass or legume species were determined. Tree xylem sap flux (F(d)') was measured by the heat pulse method. Total canopy conductance to diffusion of water vapor (G(t)) was calculated by inverting a simplified Penman-Monteith model. The different treatment effects were modeled by the simple decaying exponential relationship G(t) = G(tmax)e((-bD)), where D = air saturation deficit. At the Lincoln site, trees with an understory of cocksfoot had lower F(d)' and G(tmax) than trees with an understory of ryegrass, although the sensitivity of G(t) to increasing D (i.e., the value of b) did not differ between treatments. At the Eyrewell site, irrigation only increased F(d)' in the absence of an understory, whereas the presence of understory vegetation, or lack of irrigation, or both, significantly reduced G(tmax) and increased b. We conclude that the selection of understory species is critical in designing successful agroforestry systems for low rainfall areas.

Trees, soils, and food security

Trees have a different impact on soil properties than annual crops, because of their longer residence time, larger biomass accumulation, and longer–lasting, more extensive root systems. In natural forests nutrients are efficiently cycled with very small inputs and outputs from the system. In most agricultural systems the opposite happens. Agroforestry encompasses the continuum between these extremes, and emerging hard data is showing that successful agroforestry systems increase nutrient inputs, enhance internal flows, decrease nutrient losses and provide environmental benefits— when the competition for growth resources between the tree and the crop component is well managed. The three main determinants for overcoming rural poverty in Africa are (i) reversing soil fertility depletion, (ii) intensifying and diversifying land use with high–value products, and (iii) providing an enabling policy environment for the smallholder farming sector. Agroforestry practices can improve food production in a sustainable way through their contribution to soil fertility replenishment. The use of organic inputs as a source of biologically–fixed nitrogen, together with deep nitrate that is captured by trees, plays a major role in nitrogen replenishment. The combination of commercial phosphorus fertilizers with available organic resources may be the key to increasing and sustaining phosphorus capital. High–value trees— ‘Cinderella’ species, can fit in specific niches on farms, thereby making the system ecologically stable and more rewarding economically, in addition to diversifying and increasing rural incomes and improving food security. In the most heavily populated areas of East Africa, where farm size is extremely small, the number of trees on farms is increasing as farmers seek to reduce labour demands, compatible with the drift of some members of the family into the towns to earn off–farm income. Contrary to the concept that population pressure promotes deforestation, there is evidence that demonstrates that there are conditions under which increasing tree planting is occurring on farms in the tropics through successful agroforestry as human population density increases.

Carbon storage benefits of agroforestry systems

The process of land degradation is a local phenomenon that occurs field by field. Because of the extent at which it is occurring, however, it also has a global dimension. Agroforestry represents a link between the local and global scales. From the farmer's perspective, agroforestry can be a way to increase crop yields and the diversity of products grown. An additional benefit is the creation of a carbon sink that removes carbon dioxide from the atmosphere. Successful agroforestry systems will also reduce land clearing and maintain carbon in existing vegetation. An extensive literature survey was conducted to evaluate the carbon dynamics of agroforestry practices and to assess their potential to store carbon. Data on tree growth and wood production were converted to estimates of carbon storage. Surveyed literature showed that median carbon storage by agroforestry practices was 9 tC/ha in semi-arid, 21 tC/ha in sub-humid, 50 tC/ha in humid, and 63 tC/ha in temperate ecozones. The limited survey information available substantiated the concept that implementing agroforestry practices can help reduce deforestation.

Enhancing biomass energy use in Kenya

This paper argues that in Kenya, environmental and economic factors will favour the continued use of biomass as a primary fuel for household and institutional cooking for the next decade or longer. The paper describes several successful projects which have improved the efficiency of urban charcoal use and of rural woodfuel use. The Kenya Ceramic Jiko, a more efficient version of the traditional charcoal stove, is a model programme sustained by free market competition, artisans participation, and widespread public acceptance. The Maendeleo stove is the best example of a successful rural woodstove project. The performance attributes of the stove, and its promotion through Kenya's largest women's organization, have resulted in the distribution of an estimated 26 000 Maendeleo stoves. Rural stove efficiency will become important as the cash-based economy expands in those areas. Agroforestry will also be critical to an enhanced use of biomass energy in Kenya. Experience to date shows that successful agroforestry programmes will have to be appropriate to local conditions and crops.

Soil erosion under a successional agroforestry sequence: a case study from Idukki District, Kerala, India

The Western Ghats of Kerala have been settled over the past 40 years by landless immigrants. Natural forests and cardamom (planted under forest canopy) have been widely replaced by small-holder cultivation. Settlers plant cassava and other annuals in the initial 3–5 years following clearing of the forest canopy. These crops are gradually replaced by black pepper, the dominant crop 5–15 years after clearing. Finally, other perennial crops, planted during the period when pepper was dominant, mature. A highly mixed “home garden” cropping phase is most common on sites 15–20 years after the forest canopy was removed. Soil erosion on sites cleared 1–3 years previously averaged 120 t/ha in the 1988 monsoon season. Over the same period, soil erosion under mature cardamom, pepper and mixed cultivation averaged 0.65, 3.5, and 1.45 t/ha respectively. Erosion levels appear to be related to cover at ground and intermediate (1–4 m) heights above the surface. Soil organic matter is high in the cardamom areas, declines rapidly when the forest canopy is cleared, remains low in pepper, and appears to rebuild to levels as more mixed agroforestry systems become established. Overall, there appears to be a succession in which high erosion and declining organic matter levels are temporary features associated with the conversion of sites from forests and cardamom to other phases.

Agroforestry systems with potential for acid soils of the humid tropics of Latin America and the Caribbean

About 34% of Latin America is occupied by humid tropics which have a high proportion of acid soils (81%). The most widespread soil constraints in the region are aluminium toxicity (69%), phosphorus deficiency (50%), severe erosion hazard (17%), low nutrient reserves (72%), and poor drainage and flooding hazard (25%). Agroforestry research on acid soils of the humid tropics is very limited, and most statements about tree/soil relationships are still supported by only sparse or indirect evidence. The basic soil agroforestry hypothesis implies that appropriate agroforestry systems improve soil physical properties, maintain soil organic matter, and promote nutrient cycling. For well-drained acid soils of the humid tropics a successful agroforestry option should be adapted to the main soil constraints. Four options selected in this paper appear to be suitable for acid soils: tree plantations, fruit-tree-based production systems with intercropping, alley cropping and improved fallows. A low-input system is suggested during the establishment period of agroforestry systems, providing cash income and ground cover.