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AgroforestSyst(2012)84:227–242 DOI10.1007/s10457-011-9452-x Strategies and economics of farming systems with coffee in the Atlantic Rainforest Biome Helton Nonato de Souza • Jan de Graaff • Mirjam M. Pulleman Received:14April2011/Accepted:31October2011/Publishedonline:19November2011 (cid:2)TheAuthor(s)2011.ThisarticleispublishedwithopenaccessatSpringerlink.com Abstract IntheZonadaMataofMinasGeraisState, data on the production value and costs of labour and Brazil,familyfarmersareadjustingtoagroecological material inputs. The results showed considerable principles to reconcile sustainable agriculture, liveli- diversityinfarmingstrategiesandmanagementamong hood improvements and biodiversity conservation. the farmers. Early adopters of AF had diversified Starting in 1993, experimentation with coffee agro- towards production of different marketable products. forestrywasgraduallyinitiatedonanincreasingnum- TheuseofnativetreesinAFforthispurpose,andfor beroffarms(37intotal),resultinginthesimultaneous restorationofsoilfertility(e.g.,leguminoustrees),had management of sun coffee (SC) and agroforestry increased since the start of the experiments, while coffee(AF)plots.Weaimed(1)toidentifyfactorsthat exotic tree species were eliminated. Over a period of determine the farmers’ selection of trees used in AF; 12 years AF was more profitable than SC due to the (2)todescribetheagroecologicalfarmsintransition; productionofadiversityofagriculturalgoods,despite and(3) toperform aneconomiccomparison between somewhat higher establishment costs. Other ecosys- AF and SC. These objectives were addressed by temservicesdeliveredbyAF,suchasbiodiversityand combining data from botanical surveys in 1993/1994 culturalservicesarecurrentlynotvalorized.Payment and2007,byinterviewswithfarmersandbydetailed schemes for environmental services could further improve the economic benefits of AF for family farmersandalleviateestablishmentandlearningcosts. Keywords Familyagriculture(cid:2)Coffee agroforestry(cid:2)Productivity(cid:2)Profitability(cid:2) H.N.deSouza(cid:2)M.M.Pulleman Ecosystemservices DepartmentofSoilQuality,WageningenUniversity, P.O.Box47,6700AAWageningen,TheNetherlands PresentAddress: H.N.deSouza(&) Introduction QMSW4,lote3,Apto103,SetorSudoeste,Bras´ılia, DF70.680-400,Brazil e-mail:[email protected] Povertyandfoodsecuritydependonthefunctionsand services that local ecosystems supply (Sala and J.deGraaff Montes 2007; SSNC 2008). However, the ability of LandDegradationandDevelopmentGroup,Wageningen ecosystems to secure human well-being has declined University,P.O.Box47,6700AAWageningen, TheNetherlands (MEA 2005). Increasing food production while 123 228 AgroforestSyst(2012)84:227–242 reducing the dependency on fossil fuels, protecting opportunities for certification of shade-coffee (Per- wildlifespeciesandenhancingenvironmentalquality fectoetal.2005;Vaastetal.2006). is an important challenge for today’s society. As an However,on-farmstudiesoftheeconomicaspects alternativetothecurrentmodelthatfocusesprimarily (including productivity, labour inputs and profitabil- onmaximization ofproductionofagriculturalgoods, ity) of AF are scarce and documentation of local new forms of agriculture that strengthen the delivery knowledge on management strategies and tree selec- of multiple ecosystem services (ES) are being advo- tionislargelylacking(Molua2005;Jose2009).This cated (Lundberg and Moberg 2008; Brussaard et al. typeofknowledgewouldbecrucialforscalingupAF 2010).Interdisciplinaryscience,agriculturalmanage- coffee production and to inform agri-environmental ment interventions and institutional development at andruraldevelopmentpolicies(Molua2005;Bennett local and global scales are needed for ecological andBalvanera2007). intensificationofagriculturalproduction(Perfectoand Our study focused on the Zona da Mata (ZM) Vandermeer 2008; Carpenter et al. 2009), but many region,locatedintheAtlanticRainforestbiodiversity questionsconcerningthetrade-offsbetweeneconomic hotspot (Myers et al. 2000) and characterized by the andecologicalbenefitsremain. predominanceoffamilyfarms.Sustainableagriculture Indevelopingregionsfamilyagricultureisusually is of vital importance for the ZM, where the side based on low external inputs and therefore strongly effects of the ‘‘green revolution’’ have caused severe linked to internal resources and ecological processes environmental,agriculturalandsocialproblems(Fer- (SalaandMontes2007).Fortheseconditionsfarming rari 1996). Biodiversity loss in ZM is the result of a practices based on agroecological principles (i.e., hugeloss andfragmentationofforestcover ofwhich optimizingtherecyclingofbiomassandnutrientsand only 12–14% remains today (Ribeiro et al. 2009; enhancingspeciesandgeneticdiversityandbeneficial Teixeira et al. 2009). Participatory experimentation interactionsamongbiologicalcomponents)inorderto with agroecological principles has started in 1993, maintainproductivitywithminimaluseofagrochem- with the aim to enhance crop diversification, soil icals and other external inputs have been promoted restoration, and biodiversity conservation on family (Egohetal.2008;Schrothetal.2009).Agroecological farms.Furthermore,farmers,togetherwithNGOsand practiceshavebeenadvocatedastechnologiesthatcan university researchers started an agroecological simultaneously offer environmental, social and eco- transition process, making gradually adaptations on nomic benefits to human beings and support the their farms converting them from the conventional conservationofwildlife(Harveyetal.2008;Ouinsavi approachtomoreecologicallybasedsystems.Aspart and Sokpon 2008). In particular, agroforestry (AF) ofthisexperimentationAFcoffee(CoffeaarabicaL.) can combine production functions with biodiversity systems have gradually been established on an conservation by connecting fragments of remaining increasing number of farms (37 in total; Souza et al. naturalforestinthelandscape(Bucketal.2006). 2010,Cardosoetal.2001). In the past, coffee in most areas in Latin America Considering low external input systems and the was grown under the shade of a diverse tree canopy, relationships between biological components of an providingvarious environmental benefits.Inyearsof agroecosystem in terms of supplementarity, comple- lowcoffeeprices(andrelativelyhighfertiliserprices) mentarityorcompetition(Conway1987;Filius1982), thetreeswereallowedtoprovidemoreshade,whilein we hypothesized that AF systems have a higher years of high coffee prices the shade trees were productivity (here defined as the harvested products severely pruned, more fertilisers were applied and perunitofarea)andprofitability(definedasthegross higher coffee production was obtained. With the marginperunitofareaandpermanday)thanSC. introductionofnewhighyieldingcoffeevarieties(mid Theaimsofthisstudywereto:(1)identifyfactors of twentieth century) full sun coffee was more that determine the farmers’ selection of trees in generally applied and this is particularly the case in agroforestrysystems;(2)describethefamilyfarming Brazil. In more recent years renewed attention is systems in agroecological transition and (3) perform paid to the environmental and biodiversity benefits aneconomiccomparisonbetweencoffeeagroforestry of intercropping with multiple tree species and systemsandconventionalcoffeeproductionsystems. 123 AgroforestSyst(2012)84:227–242 229 Materialsandmethods conventionally managed systems to systems based onagroecological principles.One ofthese systemsis Studysite coffee agroforestry (AF), in which coffee plants are intercroppedwithtrees,shrubsandherbaceousplants. TheZonadaMata(ZM)islocatedinthestateofMinas The main functions of the trees are protection of the Gerais(MG)andhasatropicalhighlandclimate.The soil against erosion, recycling of nutrients and diver- average daily temperature is 18(cid:3)C and the average sification of production. AF and SC systems are precipitation is 1,500 mm year-1, with 2–4 dry managedside-by-sideonthesamefarm. months. The slopes range from 20 to 75% and the altitudefrom200to1,800 m(Golfari1975).Themain Selectionofthefarmsandfarmingsystemsforthis soil types are Oxisols, which are deeply weathered, study well drained, acidic and poor in available nutrients (Cardosoetal.2003).Around18%ofthepopulationin Within ZM there is a group of about 600 families, ZM lives in the countryside, mainly on family farms distributed over 20 municipalities, involved in agro- (IBGE2000).Theaveragefarmsizeis18 haand91% ecological transition throughcollaboration with local of the farms has less than 100 ha (IBGE 2000). The non-governmental organizations (NGOs), farmers’ characteristics of agricultural production in ZM are: organizations and research institutes (Cardoso et al. long-term land use, small-scale production systems, 2001).Thesefarmsserveasaplatformforknowledge and conventional agricultural practices, mainly for exchange and study of the effects of agroecological coffeeproductionandcattle. practices on productivity and profitability of farming In the nineteenth century the rainforest was systems and of the environmental services provided. replaced by agriculture, mainly due to favorable From these 600 families, a group of 100 families climate and market conditions for coffee production belongtoa‘‘MonitoringProgramontheSustainability (Dean 1995). Few forest fragments are conserved as ofAgroecosystems’’conductedbytheNGOCentreof forestreservesandcoffeeplantationsextendtothetop Technologies Alternatives of Zona da Mata (CTA- of the hills. Such deforestation has caused loss of ZM) and partners (CTA-ZM 2006) with the aim to biodiversityandsoilerosion,leadingtodrasticlossof document changes in management practices on the soilfertility(Dean1995). farms. From these 100 families, three sets of farms Conventional full-sun coffee (SC) is the predom- wereincludedinthestudypresentedhere(Table 1). inant type of coffee production. However, family Thefirstgroupwasformedbythosefarmsonwhich farmers that have participated in a participatory botanical surveys were carried out in AF plots in the projectthathasrunsince1993(Cardosoetal.2001), early stage (1993/1994, 15 farms, group 1a) and have changed at least part of their land from approximately 13 years later (2007, 7 farms, group Table1 Studydesignforthispaperconsideringthedifferentgroupsofselectedfarmers,datasetsusedforeachtopicofinvesti- gationandtherelatedobjectives Group Numberof Dataused Topicofinterest Objective familyfarms 1a 15 Botanicalsurveyconductedin:1993/94 Determinantfactorsfortheselection 1 1b 7 2007 oftreestoimproveperformanceof regionalagroforests 2 6 Farmingactivities,management,farmlayout,inputs Descriptionoffamilyfarmsin 2 andoutputsobtainedthroughparticipatory agroecologicaltransition techniques(interviews,flowdiagram,maps) 3 3 Coffeeproduction,labour(demand?costs), Economiccomparisonbetween 2and3 sales,spending agroforestryandconventionalsystems a Regionalreferencesofcoffeeagroforestryexperimentsestablishedatinitialphase b Bestregionalperformersofcoffeeagroforestryexperimentsatlaterstageofexperimentation;inthisgroupof7,twofarmsofthe groupof15areincluded 123 230 AgroforestSyst(2012)84:227–242 1b). Although the overlap between the two groups is the early adopters. These three farms maintained only two farms, the use of two sets of representative parallellong-termAFandSCexperimentswithineach farms allows for the interpretation of changes in farmandwerecomparableintermsofslopeandageof compositionofcoffeeAF,byconsideringtheexisting the coffee plants. These three families were living data on tree species and their uses by local farmers undersimilarsocialandeconomicconditions. overalongperiodofexperimentation(objective1). A second group of farmers implemented agroeco- logical practices in the period 2003–2005 and was Datacollection composed of 6 families (Farms 1–6; Fig. 1), which volunteered (one family per municipality) to partici- Changesintreecomposition pate in a specific activity inserted in the monitoring program mentioned above, which should reveal Twobotanicalstudieswereusedtoassessthechanges ‘‘indicatorsofsustainability’’. that occurred in tree family composition across the Athirdgroupwasformedbythreefamilies(Farms AFs established between 1993 and 2007. Franco A1, A2 and D1; Fig. 1). These belonged to the early (2000)conductedthebotanicalsurveyin15ofthe37 adoptersofAFinZMandstartedin1993/1994(Souza initial AF experiments established in 1993–1994 and 2006).Informationonfarmingpracticesandmanage- Siqueira(2008)studiedthe7bestdevelopedAFplots, mentfromthesecondandthirdgroup(9farms)were assuggested by local farmersin2007. Thefarms A1 usedtoaddressobjective2. andA2wereincludedinbothsurveys.Informationon For the economic comparison of AF versus SC uses of trees was obtained through a participatory systems (objective 3) we focused on the third group, appraisalamongfarmers. Fig.1 LocationoftheselectedfarmsinsixmunicipalitiesoftheZonadaMata(ZM),MinasGeraisstate,Brazil 123 AgroforestSyst(2012)84:227–242 231 Farmcharacterization calculatedbasedonthefarmers’individualnotesand the number of trees existing in each AF system was The six farmers of group 2 recorded the data on counted. Elevation and slope of the farms were consumption, production, income, farm layout and measuredwithGPSandclinometers. subsystems, crops, inputs, outputs and the annual Thestepsusedfortheanalysisofproductioncosts calendaroffarmingactivitiesandsharedthemduring are based on Duarte et al. (2004), in which the several meetings held between 2005 and 2006. The Production value A minus the costs (B ? C?D ? threefarmsofgroup3werevisitedin2008toobtain E ? F ? G)isequaltoGrossMarginI.Belowmore the same information. During the visits the flow detailsaregivenfortherespectiveitemsAuntilJ: diagramtechnique(Geilfus2000)wasused.Theflow A. Total production values: the production values diagram provides an evaluation of all inputs and were obtained by considering all marketable outputs of the agroecosystems, including both the products produced during 1 year. The prices of material inputs and services and the products pro- theseproductswereverifiedinthelocalmarketof duced. It also allows the identification of the links of ArapongaandDivinoduringFebruaryandMarch farmingsystemswiththeotheragroecosystemsofthe 2008. property(Geilfus2000).Thediagramsweredrawnby B. Annuities of establishment costs were calculated thefamiliesduringtheinterviews.Thiswasfirstdone based on the activities (person days) and mate- for each individual subsystem, and thereafter for the rials (material costs) required to establish the wholefarm. differentcoffeesystems.Onefarmerbelongingto The nine farmers of groups 2 and 3 provided the the first group of 6 farms had accurately docu- resultsofthelastsoilanalysisforthecoffeeplots(SC mented allactivities related tothe establishment and AF) carried out in the labs of the Soil and Plant of his SC and AF systems. We used his data to NutritionDepartmentofFederalUniversityofVic¸osa calculatetheestablishmentcostsoveraperiodof in2005/2007.Therange ofsoilcharacteristicsof the 3 years.Basedontheinformationprovidedbythe farmsispresentedinTable 2. farmerswesetthelengthoftheproductioncycle Thethreefarmsofgroup3fellwithintherangeof at12 yearsforbothsystems. soilcharacteristicsfoundforgroup2(Table 2).Group C. Labourfor croppingcoversthe annual activities 3 (early adopters) presented less variation in nutrient requiredforthecashcrop(coffee),othercropsor andorganicmattercontentandgenerallyhighervalues products, and the production of compost. The thangroup1(Table 2). prevalentdailywagerateintheregionisR$20.00 adayorUS$11.00dollar(March2010). Analysisofproductivityandprofitability D. Intermediate consumption included all expenses forexternalinputsnotproducedonthefarm(e.g., DuringthevisitsoffarmsA1,A2andD1inFebruary fertilizers, lime, bio-fertilizers, compost, bags, and March 2008, more detailed information used for andboxes). the economic comparison (objective 3) was also E. Processing costs were the total cost of post- collected.Theannualaverageproductionofthemost harvestactivitiesforallproductsonthefarm.The important products over 3 years (2005–2007) was costs of coffee drying on the ground was Table2 RangeofsoilcharacteristicsforselectedfarmsinZonadaMata,Brazil Farms Period pH P K Ca Mg CEC1 BSat2 OM3 (1:2H.25O) (cmolcdm-3) (cmolcdm-3) (mgdm-3) (mgdm-3) (mgdm-3) (%) (%) Group2a 2005/6 4.9–6.6. 0.4–7.6 29–161 0.3–5.4 0.2–1.7 7.2–19.0 6.3–85.0 2.7–5.3 Group3b 2007 5.6–6.0 2.7–4.8 89–164 2.8–5.7 0.6–1.5 3.6–7.6 30.0–76.0 4.3–5.7 Codes:CECcationexchangecapacity,basesaturation,OMorganicmatter a Farmsinagroecologicaltransition(1–6) b Farmsofearlyadopters(A1,A2,D1) 123 232 AgroforestSyst(2012)84:227–242 calculatedatUS$1.67bag-1(onebag = 60 kg) (Souza2006).Changesintreecompositionovertime, for coffee in the early processing stages called since the start of the on-farm AF experiments in the ‘‘cafe´ emcoco’’(Bliskaetal.2009). early1990s(Franco2000)until2008(Siqueira2008) F. Overheadswereconsidered2.5%ofintermediate are shown in Fig. 2. The respective uses of each tree consumptionfollowingBliskaetal.(2009). familyareindicatedatthebottomofthegraphandare G. Interest on circulating capital was defined as based on the information provided by the farmers 12%ofthesumofintermediateconsumptionand during semi-structured interviews (Fig. 2). Several overheadcosts(Bliskaetal.2009). exotictreespeciesthatwerefoundintheAFsystems H. Total person days is the time spent (including in 1993/1994 were not present in the AF systems temporaryworkers)onfarmingactivities. monitored in 2007 (e.g., Casuarinaceae, Ebenacea, Myrsinaceae, Pinacea and Caprifoliacea) (Fig. 2). Gross margin (GM) was calculated by deducting Farmers reported that they had been eliminated the variable costs and also some fixed costs because of their different requirements in terms of (B ? C ? D ? E ? F ? G) from the total produc- climate and soil conditions that led to increased tion value (A). A distinction is made between ‘‘GM competition with, or damage to, coffee plants. Tree including labour’’ (I), whereby labour costs are also familiesthatprovidemultipleproducts,suchasfood, deducted and ‘‘GM excluding labour’’ (J) whereby wood, green manure, medicine and other products labour costs are not deducted. The gross margin per (e.g., fibre, oil, seeds), were kept or added (e.g., person day is obtained by dividing ‘‘GM excluding Bignoniaceae, Rutacea, Myrtaceae, and Euphorbia- labour’’,bythetotalnumberofpersondays.Thiscan ceae).Localavailabilityandmarketopportunitiesare becomparedwiththeprevalentwagerate. determining factors for selecting those trees with multipleuses. The initial AF experiments on 15 family farms Results (group 1a) started with a minimum of 2 and a maximum of 72 tree species per AF plot, belonging Treecompositionandtreeselectioncriteriaattwo to a total of 34 different tree families (Fig. 2). This differentstagesofimplementation widerangeinthenumberoftreespeciesreflectsahigh diversityofapproachesbydifferentgroupsoffarmers DuringimplementationoftheinitialAFexperiments, due to the high uncertainty resulting from lack of thefarmerstogetherwithalocalNGOanduniversity experience. One group decided to start with planting researchers, focused on the following factors when fewtreespeciestoavoidrisks.Intheoppositeextreme selecting trees for the AF systems: (a) stability/risk there was another group of farmers that decided to alleviation, (b) avoiding nutrient competition, and experiment with a large pool of tree species to be (c) maintaining or increasing coffee production intercroppedwithcoffee.Thirteenyearslater7family Fig.2 Theproportional 30 2007 distributionandtheusesof 15 treesinAFsystemsas 8 1993-1994 Food obtainedfrom15and7 Wood 6 farms,surveyedin Fertilizer 1993–1994and2007, % Other products 4 Medicine respectively 2 0 LeguminoseaeMusaceaeAnacardiaceaeLauraceaeMalvaceaeSolanaceaeBignoniaceaeRutaceaeMyrtaceaeEuphorbiaceaePalmaeCaricaceaeRosaceaeAnnonaceaeSapindaceaAraucariaceaeBixaceaeVerbenaceaeLamiaceaeUrticaceaeMoraceaeMeliaceaeelastomataceaeRhamnaceaeAsteraceaeApocynaceaeMoringaceaeCannabaceaeMalpighiaceaeCasuarinaceaeEbenaceaeMyrsinaceaePinaceaeCaprifoliacea M Uses: 123 AgroforestSyst(2012)84:227–242 233 farms(group1b)reporteddifferentcriteriaforselect- AFcoffeeproductionin2005becausethatwasthefirst ingtreesthanthoseinitiallydefinedatthestartofthe yearinwhichcoffeewasplanted. project. Selected trees included then species that Alargevarietyofcropswasproducedoneachfarm (a)arecompatiblewiththecoffeecrop;(b)producea in AF areas. Food, firewood, water and construction good amount of biomass; (c) are soft and easy to materials are the most common needs for the family. manage (e.g., cutting, pruning, transporting), and Although such diversity contributes to local agrobi- (d) provide extra products such as food and animal odiversity, it also increases labour intensity in the feed, or (e) stimulate wildlife, as reported during the beginning, which was indicated as a constraint by 6 interviews. outof9farmers. Forest within the farms is also called ‘‘reserve’’, Generalcharacterizationofthefarmsandtheir followingtheBrazilianenvironmentallaw.However, coffeesystems wood and non-wood products can be harvested for familyconsumptiononly(e.g.,honey,seed,medicines A compilation of the individual flow diagrams (not and fibre). Together with AF as a subsystem they shown) that was obtained for each of the 9 family representedthemainsourceofwoodforconstruction farmsofgroups2and3demonstratedthatallofthem (Table 3). had diversified their farms as part of the agroecolog- icaltransition,withtheobjectivetomakethedifferent components of subsystems more closely connected ManagementofSCandAFcoffeesystems and mutually supportive to reduce the need for external inputs. These 9 families represented a range Moredetailedinformationoncoffeemanagementwas of different farm settings in family agriculture in the obtainedforthethreefarmsofgroup3(Table 4).Ona ZM. The farm size ranged from 6 to 90 ha. The yearly basis, the management activities could be number of family members, indicative for labour divided into three main periods. From January to availability,rangedfrom2to7.Sixfamilieswereland April,theactivitiesincludedthefirstsowingofsome ownersandthreeweretenants.Thetotalareaofcoffee annual crops, weeding, fertilizer application, tillage, cultivation on the different farms ranged from 1.5 to and trimming. The harvesting of beans, maize, and 9.5 ha,correspondingto4–47%ofthetotalfarmarea. cassava is done from May to July. From May till The density of coffee plants ranged from 2,310 to September,themainactivitiesaretosoilpreparation, 7,500 ha-1inSCandfrom1,785to5,333 ha-1inAF. cropmanagement(routine),foliarfertilizationandthe Thelandowners,especiallytheearlyadoptersofAF, secondsowingofbeansandmaize. hadamorediversifiedfarmintermsofthenumberof In AF the spontaneous vegetation is kept or commercialized products and the presence of own trimmed, no pesticides or herbicides are used and forest(Table 3). limestone is applied biannually. The use, type and Coffeewasthemaincash cropanddifferenttypes quantityoffertilizersdependonwhethertheAFcoffee ofcoffeeplotswerepresentatallthefarms.On7out is certified for organic production or not. Family of9farms,theareaunderSCwashigher(rangingfrom members do most of the field operations in the AF 0.9to7.9 ha)thantheareaunderAFonthesamefarm systems.TheSCsystemsdonothavetreesshadingthe (0.3–2.6 ha). Coffee planting density was distinctly coffee. In this type of system liming is done biannu- higherinSCthaninAFonfourofthefarms(farms2, ally, fertilizers are applied annually and herbicides/ 5, 6 and A2), more or less similar on the other four pesticidesareusedwhenconsiderednecessary.Some farms(farms1,4,A1andD1)andlowerinSCthanin farms apply tillage and some farms do not. Some AF on farm 3. The number of commercialized farmersintercropthecoffeewithherbaceousplants(in productsandthepresenceofforestonthefarmvaried few cases even with annual crops). It is common to depending on land tenure. Based on the farms employ temporary workers for field operationsin the considered in our study, coffee production (parched) SC systems. Soil preparation includes limestone underAFrangedfrom120to1,644 kg ha-1andunder broadcasting and manure application. In some cases SC(basedonlyontheearlyadopters’farms)itranged manual tillage is used, especially when maize is from1,320to1,602 kg ha-1.ForFarm1therewasno cultivated. All coffee systems are biannually limed 123 234 AgroforestSyst(2012)84:227–242 1 n e FarmD Divino 2 Owner 6 2.8 2.5 2,310 1,602 0.3 2,310 1,644 1993/4 Banana Beans Citrus Coffee Maize Pumpki Wood Yes 5%ofth s u systems FarmA2 Araponga 2 Owner 43 8.7 7.9 2,730 1,320 0.8** 1,785 313 1993/4 Avocado Banana Beans Cassava Coffee Maize Sugarcane Wood Yes 91.5m)pl ee 3 (AF)coff FarmA1 Araponga 4 Owner 90 9.5 6.9 3,465 1,350 2.6** 3,465 1,650 1993/4 Banana Beans Coffee Guava Maize Papaya Pumpkin Wood Yes armD1= y F str m, andagrofore Farm6 EsperaFeliz 7 Owner 8.8 2.8 1.2 7,500 NA 1.6** 1,875 630 2005 Banana Beans Cassava Coffee Eggs Maize Peanut Sugarcane Yes C3.291.2 C) S S m, ncoffee( Farm5 Guiricema 4 Owner 68 2.7 1.4 4,545 NA 1.3 2,308 1,380 2004 Beans Coffee Livestock Eggs Pumpkin Wood Yes 491.5 u F withtheirfull-s Farm4 Carangola 5 Owner 12 1.8 0.9 4,500 NA 0.9** 4,444 450 2005 Banana Coffee Honey Livestock Vegetables Yes FarmA2=A m, 3 ofgroup Farm3 Tombos 4 Tenant NA 1.5 1.2 2,833 NA 0.3 5,333 1,080 2005 Beans Cassava Coffee Maize Cassava flour No =391 s 1 m A ar ck d threef Farm2 Divino 2 Tenant 29 1.6 1.1 3,636 NA 0.5 1,800 120 2005 Beans Coffee Eggs Livesto No 1–6an d m an ar Table3Generalinformationaboutthesixfarmsofgroup2 ItemsFarm1 1.MunicipalityAraponga 2.#offamilymembers2 3.LandtenureTenant 4.Farmsize(ha)NA*5.Totalareaofcoffeesystems(ha)1.6 a.Full-suncoffee(ha)1.3-1DensityofcoffeeplantsinSC(plantsha)3,230-1Coffeeproduction(kgha)NA b.Agroforestrycoffee(ha)0.3**-1DensityofcoffeeplantsinAF(plantsha)3,333-1Coffeeproduction(kgha)– c.YearofadoptionofAF2005 6.CommercializedproductsBeans Coffee Honey Propolis 7.ForestonfarmNo NAnotavailable *Thesizecalculationwasbasedonthecoffeeplantspacing(Ftotaltocompensatespaceforinternalroads **Partofitiscertifiedfororganiccoffeeproduction 123 AgroforestSyst(2012)84:227–242 235 as as andannuallyfertilized.Thefarmerssprayhomemade e e tre tre liquid compost called ‘‘supermagro’’, as biological ng ng fertilizer in AF at least twice a year. Spontaneous OctNovDec Pruni Chemicalfertilizera,bapplication Applybiologicala,bfertilizerbSowingmaize/beansa,baLimingWeeding a,bLimingPrunia,bApplybiologicalfertilizer aAnimalmanureapplicationa,bWeeding vpatbaChnleeuhsegrdtoateyrorrtpaeeenacrseatuitisrfdeon,airunersmimedsdisatnoiiiacAnnntrslhee2Jyoeufltfreilhcnoyfsoetm.etfohlbfenDeeocettetphteceofiedermeimslSooddCbbilierNsasarunnwotorcdvfehMaeeAecmdsaeFebr.odcecTfhroahtfottehfonelepeeFarateulrslbentferiatunswragmaircoryseef,, systemsusedforeconomicevaluation b Sep a,bLiminga,Weeding manureaation Tsyhsetesmpescoififcgrcohuapra3ctfearrimstiscsaroefsthhoewAnFinanTdabSlCe 5c.ofTfheee malplic systems in each farm were established at similar ug niap elevation (ranging from 1,040 m at farm A2 to A A 1,160 m at farm D1). Slopes were steeper on farm a,beans agtrees a,bstinga,beans ATh2e(7si5z%e)otfhtahneocnofAfe1easnydstDem1s(arpapnrgoexdimfraotmely0.3445%t)o. utonthethreefarmsovertheyear MayJunJul a,bCoffeeharvesting Harvestingb a,bCleaningrowsofcrops a,bCoffeeharvesting BiologicalfertilizerPruninaapplicationbMaize/beansharvestinga,bHarvestingbeansCoffeeharve Harvestingb iAlap0shtnohyre.aF7ecasrd7Taan7.tf6eoa’th’itm%Ihroelhnmotaneshdwh,afaaieSionnwedtgnCrcrdthsahehpSiiele(.ttewl2rCiyraoeFc,pan6noaaoyrtt0fshonirsn0eteddcotgauoochA0fcffdoift.fFstehe1Afeifcnio5ewfe1stsan–ee,piara0dtpmslpnyt.ahe7ldenen(are2s1ertnDut,sg,athf7n1saatbwa0ih.trlhti0amIeifvaasnsoceh-remrAeotler1hyaAfda)2efsi,fteFwntthosweah.ahertegpameiScosplAdaCeharanFoltfrtt‘dho‘hesswucaysrahocautsnbasottl-oittefloehoettm1dhoner)r o rehabilitate the area by controlling soil erosion. Any carried a,bement ebxetcraoncsoifdfeereepdroanduacdtvioanntoabgtea.inOendtfhreomfarthmastAar1eaawndouDl1d s g coffeesystem Apr a,bFertilizing a,bCleaning Coffeemana a,bRoutine afertilizer tahhnaed-Tc13h,o%effbeAhueiFtgphrstoeyhrdsetufyeocmrtisoAdniFfcfopetnehrretaadnhinefecoidtnrarSoeCtnawx(aaTovsnaerobreamlsegpiec5ec)3.t3irvi5cehltynree1es8ss 4Mostrelevantactivitiesforboth JanFebMar bWeeding Chemicalfertilizera,bapplication Applybiologica,bfertilizeraPruningtrees Sowingbeans/bmaize a,baWeedingPruningtreesa,bApplybiologicWeedingafertilizeraPruningtreesApplybiologicala,bSowingbeans bSC o(hfirbtsOmrTaiusiecenrsabageepmtnboiflncaseulsrcepnury.mdomeliaO5tnlecoiu)gnvniAwfbe,taaesr2eftlsnidaiaronHotedrnhihemnlodeia,cnvwdaAo(AeutesnamnbsFo1rsdeieppbaesctlcoryahanodaosnnsevsufidtdttifeeleeailecro)mdgrete,ienosrdrasa,wa(Itdtbounnwwaheypvgdsedhhpaaoigie-aenmcrrrdfedthaetsrolqesoyet-uAsroisdjsiawssFusrpipeepclriravi˜tmeeaeoshoelcnddae)ridtut,anethaeoclstGnSedseydhaCl.ceanoatIoaonldfnwIfrtdnfsettttteughhhhhorelaeeeeee-f. Table Site A1 A2 D1 aAF, asodivlaanncdeddeeproossiitoendpthroecseosisl,mwahteicrihalhtaodthreemloowveedsttphaerttoopf 123 236 AgroforestSyst(2012)84:227–242 Table5 Characterizationoftheagroforestryandfull-suncoffeesystemsofthethreeearlyadoptersintheZonadaMata,Brazil Systems Elevation(m) Slope(%) Area(ha) Coffeeplantation Trees (#/ha) Plants(#ha-1) Spacing(m) Age(year) Production* (kgha-1) AFA1 1,062 33 0.15 3,300 3.091.0 12–14 1,650 380 SCA1 0.75 3,300 3.091.0 12–14 1,350 0 AFA2 1,040 75 0.72 1,700 4.091.5 12–14 317 370 SCA2 0.77 2,600 3.291.2 12–14 1,320 0 AFD1 1,160 35 0.27 2,200 3.091.5 10–14 1,644 257 SCD1 0.45 2,200 3.091.5 10–14 1,600 0 Codes:AFagroforestry,SCfull-suncoffeesystems,AAraponga,DDivino *Consideredtheaverageover3years(2007,2008and2009) the farm where it had damaged the roads and farm citrus, pumpkin, wood, and organic compost repre- buildings. The farmer planted some trees belonging sented 30% of the total production value in AF-D1, to a pioneer succession and several fruit species, whereas in AF-A1 the products banana, wood, mostly avocado (Persea americana). The farmer has avocado, cassava, sugarcane and organic compost harvestedbananas,oranges,avocados, sugarcane and representonly14%oftotalvalue(Table 6). pumpkin from the AF. This system is converted into Theannuityofestablishmentcostswasonaverage an organic system and the coffee plants have been 17% higher for the AFs than for the SCs due to the rejuvenatedonce,inthebeginningoftheexperiment. increased labour for other crops (Table 6). Labour is The system has a low density of coffee plants the most expensive factor during this phase contrib- comparedtotheothertwofarms.Chemicalfertilizers uting on average 58% of establishment costs in both werenotappliedinthissystem. systems,overthefirst3 years.Theestablishmentcosts ThefarmerofD1plantedsomepioneertreesinhis of other crops are on average 11% of the total AFsystemandtherewerealready somematuretrees establishment costs (data not shown). The labour from secondary succession, such as Zeyheria tuber- required for annual cropping was higher for AF than culosa (ipeˆ-preto), Tabebuia sp. (ipeˆ-amarelo) and for SC, varying from 136 to 202 person days ha-1 Vitex montevidensis (maria-preta). This area was year-1 in AF, and from 99 to 134 person days ha-1 originally an abandoned pasture. Bananas, oranges year-1 for SC. The intermediate consumption val- and avocados have been harvested from the AF. The ues largely depended on the management, arrange- trees also supply wood for construction, firewood, ment and level of external inputs of the farming fencingandanimalfeed. systems (e.g., chemical fertilizers, lime, liquid com- post, fuel and electricity cost). While AF-A1 (US$ ProductionvaluesandgrossmarginsinAFandSC 641 ha-1 year-1), SC-A1 (US$ 631 ha-1 year-1), systems AF-D1 (US$ 851 ha-1 year-1) and SC-D1 (US$ 841 ha-1 year-1)havequitesimilarexpensesinboth The total production value was higher for all AFs systems, in AF-A2 the intermediate consumption (ranging from US$ 4,976 to 6,281 ha-1 year-1) in value is much lower (US$ 158 ha-1 year-1) than in comparison to all SCs (ranging from US$ 3,534 to SC-A2 (US$ 522 ha-1 year-1), mainly because no 4,284 ha-1 year-1) (Table 6). The production value chemicalfertilizersareusedinAF-A2. forAF-D1wasabout20%higherthanforAF-A1and Regarding the processing costs, more labour is AF-A2. For SC-D1 the production value was about required for coffee than for other products (e.g., 17%highercomparedtoSC-A1andSC-A2. drying, bagging, post harvest preparation, transport). In AF-A2 other products than coffee, including Thecostsoftotalmaterialinputsdependedonthetype banana, papaya, pumpkin, citrus, wood, and guava, of crops, frequency of cultivation and care needed. made up 73% of the total production value. Banana, The values were higher for AF on all three farms. 123

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(Egoh et al. 2008; Schroth et al. 2009). Agroecological practices have been advocated as technologies that can simultaneously offer environmental, social and eco- nomic benefits to systems in agroecological transition and (3) perform Dean W (1995) With broadax and firebrand: the destruction of.
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