Frontiers in Conservation Tillage and Advances in Conservation Practice Rolf Derpsch Introduction Constraints and limitations for no-tillage adoption in South America and how they have been overcome Primary needs associated with the technologys further use and adaptation and constraints to extensive use. Introduction Control of soil erosion is still one of the main driving forces for no-tillage adoption. No technique yet devised by mankind has been anywhere near as effective at halting soil erosion and making food production truly sustainable as no-tillage (Baker et al., 1996). The long term gains from widespread conversion to no-tillage could be greater than from any other innovation in third world agricultural production. (Warren, 1983). General situation of
no-tillage in the world Table 1: Total area under No-tillage in
different countries (hectares)
Source: 1) Dan Towery, CTIC, 2000; 2) FEBRAPDP, 2000; ; 3) Bill Crabtree, WANTFA, 1999; 4) Datos preliminares AAPRESID, 2000; 5) Dan Towery, CTIC, 1999; 6) Proyecto Conservación de Suelos MAG - GTZ, 1999; 7) Ramón Claverán, 2000; 8) Dr. Patrick Wall, 1999; 9) Carlos Crovetto, 1999; 10) Roberto Tisnes, 2000; 11) Boletin Inf. DIEA, MGAP, AUSID, 1999; 12) Estimativas. Remark: Some data on the area under No-tillage in Canada shows 6.7 million ha in that country. These numbers do allow for fall tillage with high soil disturbance. When applying the term no-tillage more strictly (low disturbance and no fall tillage) then the area is only 4.08 million ha for Canada. Although the biggest area under No-tillage is found in the USA, in this country the technology is applied only on 16,3% of the total cultivated area, against 21% in Brazil, 32% in Argentina and 52% in Paraguay. In relation to the total cultivated area, Paraguay has the highest adoption rate of no-tillage in the world (Figure 1). A study of the potential use of no-tillage in Africa has been made by GTZ in 1998. The study concludes, that no-tillage ensures optimum soil protection and is therefore the system of choice for those regions where sufficient biomass can be produced to provide all-year-round ground cover. The ecological constraining factors for spreading no-tillage in this continent are: low precipitation with low biomass production, short growing seasons, sandy soils with tendency to compaction and soils at risk of waterlogging. The socio-economic constraining factors are: strong demand for crop residues as forage for livestock, uncertain land use rights, poorly developed infrastructure (market, credit, extension service), distinct market preference for one crop (e.g. maize), and high demand on the farm management. The study also concludes, that in regions and under conditions where no-tillage is not possible, the second best choice is minimum tillage (GTZ, 1998). While no-tillage was researched in the USA already in the 1940s and more intensively in the late 1950s, and in Europe in the 1960s and 1970s, it was not until 1971 that research on this technology started in Brazil and Latin America (Derpsch, 1998). At first no-tillage was conceived as an efficient technology for soil conservation, since the spread of arable farming had brought about the widespread occurrence of erosion in the southern states of Brazil. With time the technology has evolved to a truly sustainable production system with positive economic, environmental and social consequences. In the MERCOSUR Countries (Brazil, Argentina, Paraguay and Uruguay) the technology has experienced a twenty fold expansion between 1987 and 1997 against a 4,6 fold increase of the area in the USA in the same period (Figure 2). From 1997 to 1998 the MERCOSUR Countries experienced an expansion of 28% of the area under no-tillage as against 3,7% in the USA. The following may be the main factors that induced such a rapid change in Latin America: 1) Efficient and economic erosion control under climatic conditions with high erosion and soil degradation potential. 2) Appropriate knowledge was available in the region through research and development as well as farmers experiences. 3) Widespread use of cover crops for weed suppression (reduction in the use of herbicides), organic matter build up, biological pest control, etc. 4) The same consistent message, positive to no-tillage has generally been voiced by all sectors involved (private and public) without contradictions. 5) No-tillage has been the only conservation tillage technology recommended to farmers. 6) There has been an aggressive farmer to farmer extension through farmers associations. 7) Publications with adequate, practical and useful information were made available to farmers and extensionists. 8) Economic evaluations with system approach showed high economic returns of no-tillage, as well as the use of cover crops and crop rotations in the system. Economic returns are immediate and substantial. 9) There have been no major forces against the system. 10) Latin American farmers have had to be very competitive in the global market, since in general there are no subsidies. Constraints and limitations for no-tillage adoption in South America and how they have been overcome Adequate machines For small and medium sized mechanized farms we would recommend that farmers buy a no-tillage machine suitable for wide row crops (i. e. soybeans, maize, sorghum, sunflower) and for narrow row crops (wheat, oats, rye and green manure cover crops in general). Failure in buying a multipurpose machine puts farmers that do not have enough capital to buy two specialized machines in a situation where they cannot plant narrow row crops and therefore they are not able to seed small grains or green manure cover crops and use adequate crop rotations. Leaving the land in fallow during winter time results in high weed infestation and high costs to eliminate these weeds. Adequate herbicides The production and availability of a greater variety of more efficient herbicides together with a greater diversity of more efficient no-tillage seeding equipment in Brazil and Argentina has led to an unprecedented growth of no-tillage in South America. Mental change Knowledge Herbicides Weeds Herbicide application technology Soils Concepts about liming and fertilization have changed a lot in Latin America after shifting to the no-tillage system. Experience shows us that we have to forget everything we have learned in the University about fertilization and liming and get acquainted with the new concepts in fertility management in this system. Pioneer farmer Nonô Pereira of Ponta Grossa, Paraná, Brazil, together with the soil scientist Joao Carlos Moraes de Sá have developed a system of no-tillage into native pasture, on soils that have a high aluminum saturation, low pH and in general low fertility levels (Farmers spray off the native pasture 3 to 4 months before seeding to ensure a good kill of woody grasses). Despite this fact, farmers applying relatively low amounts of lime on the soil surface and using medium fertilizer levels, can harvest around 3.000 kg/ha soybeans already in the first year. This is probably due to the high organic matter content of these soils, that have never been touched by tillage tools before. Similar experiences are now being made on poor, acid soils and native pasture in Paraguay. Soil crusting:In general crusting of soils is not a problem in no-tillage. Because the mulch cover avoids the direct impact of the raindrops on the bare soil surface crusts do not develop. We have found, that soils which very badly tend to crusting in conventional tillage do not present crusting problems in no-tillage, as long as the soil is well covered with sufficient plant residues. It is general knowledge that badly drained soils are not suited for no-tillage. Luckily most tropical soils in South America are well drained and are generally well suited for this technology. Soil surface roughness Soil compaction Soil compaction in permanent no-tillage is an issue that is discussed over and over again in Latin America. We have found that in general researchers have a different perception than farmers in looking at this problem. Since researchers have very sophisticated tools to measure compaction and easily demonstrate that soils are more compact under no-tillage than under conventional tillage, we have seen that many researchers see compaction as a very serious problem in the no-tillage system. We are observing that in general scientists and researchers in Latin America tend to overstate the problem of soil compaction. In contrast to researchers, farmers in Latin America measure compaction not in terms of soil density in g/cm3 or in penetration resistance but in terms of crop response and yields. If yields are as good or better in no-tillage than in conventional tillage, the farmer does not care about compaction. Also farmers measure compaction in terms of penetration of seeding equipment into the soil. If soils are too hard to give good penetration to the cutting elements of a planter than the farmer is going to have a bad stand. For the purpose of evaluating farmers perception on the problem of soil compaction, three no-till pioneer farmers from Brazil where interviewed in 1997 to express their views on this problem. The interviewed farmers were Nonô Pereira (22 years of permanent no-tillage), Frank Dikstra (22 years of continuos no-tillage) and Herbert Bartz (26 year of continuous no-tillage), totaling 70 years of experience. Their soils vary from about 80% sand to about 80% clay. The farmers were unanimous in stating, that they do not perceive compaction as a problem in permanent no-tillage (Revista Plantio Direto, 1999). They also stated that there is no need to till the soil every so often after no-tillage has been established. Finally they said, that the best way to avoid compaction in the no-tillage system is to produce maximum amounts of soil cover, use green manure cover crops and crop rotations, so that roots and biological activity as well as earthworms and insects, etc., loosen the soil. Good soil cover is also essential to maintain higher moisture content on the soil surface and this will result in better penetration of cutting elements of the seeding equipment. Mulch cover Besides the limiting factors mentioned a farmer also has to learn about the influence of no-tillage on chemical, physical and biological soil properties, its impact on surface water and the environment, on yields and most important on the economics of the system. Several comprehensive publications with research results have been published in the region since 1981, i. e. IAPAR, 1981; Derpsch, et al., 1991; Crovetto, 1996; Panigatti, et al., 1998; etc. Also the proceedings of many conferences held in Argentina, Brazil, Chile and Paraguay are available for detailed information on the performance of the system. In this respect AAPRESID in Argentina and FEBRAPDP in Brazil (the Federations of no-till farmers in both countries), have contributed strongly in the diffusion of site specific knowledge on the system and have helped greatly to spread the technology all over Latin America. Primary needs associated with the technologys further use and adaptation and constraints to extensive use. Crop rotations and green
manure cover crops Research conducted in southern Brazil shows consistent reductions in weed infestation with crop rotations in no-tillage and conventional tillage (Table 2). Table 2: Number of weeds per m3
with and without crop rotation in two tillage systems in Rio Grande do Sul, Brazil (
Ruedell, 1990, adapted by Gazziero, 1998)
NT = No-tillage, CT = Conventional tillage Good no-till farmers in Latin America see it as good farming practice to use GMCCs and crop rotations independently of the price situation of crops. Once farmers have discovered the benefits of these practices they dont want to miss them. Sorrenson (1984), between others, has clearly shown the economic advantages of using crop rotation and the right cover crops. While many people still think that when using GMCCs you are adding costs without getting anything back, farmers especially in Brazil and Paraguay have learned that economics of no-tillage can be substantially increased with their use. Research conducted by Kliewer (1998) in Paraguay has shown, that crop rotation and short term GMCCs can reduce the cost of herbicides drastically to US$ 36,62/ha in the case of Crotalaria juncea (52 days GMCC) and to US$ 37,39 in the case of sunflower (57 days GMCC), as against costs of US$ 107,66 when only herbicides and monoculture were used. Kliewer (unpublished, 1998) also reported soybean yields after black oats of 2600 kg/ha without using any herbicides at all. Weed measurements 96 days after seeding soybeans showed 93 kg/ha of dry matter of weeds/ha after black oats, as against 7390 kg/ha after fallow. In the last case soybeans yielded not more than 780 kg/ha. Using a rotation where long and short term GMCCs or cash crops are seeded as soon as possible after harvesting the previous crop, or after rolling down GMCCs with a knife roller, it was possible not to use herbicides in no-tillage for as much as three years in a row. In some cases when farmers are using crop rotations, only eliminating weeds with a total herbicide before planting is necessary without any herbicide application during the growing season at all. If some weeds escape, the few weeds that develop can be efficiently and economically controlled by hand hoeing because labor is cheap. Research conducted in Brazil has shown that black oats used as a green manure cover crop before soybeans can increase soybean yield by as much as 63% as compared to soybeans after wheat (Derpsch, et al., 1991). Good knowledge about green and dry matter production and profitability of green manure cover crops, how to fit them into different crop rotations and what residual fertilizer effect we can expect of each GMCC planted before the main cash crops is essential for dissemination of their use. Several publications have contributed in filling this knowledge gap mainly in Brazil (Sorrenson and Montoya, 1984; Monegat, 1991; Derpsch, 1991; Derpsch and Calegari, 1992; Calegari et al., 1992). Lessons learned GMCCs and crop rotation are the key factors for the unprecedented growth of no-tillage especially in Brazil and Paraguay. Linked to the spread of cover crops is the use of a "knife roller" to put the cover crops down to the ground. This implement is not terribly expensive and in many cases can be made locally or by the farmer himself. The implement can be pulled by medium sized tractors or by animal traction and has contributed a lot in reducing herbicide rates in the no-tillage system. The knife roller has become an essential tool for managing GMCCs in many countries of South America. Alternatively steel bars can be welded on top of the discs of disc harrows and the implement used for the same purpose. New developments Finally we have to admit that all over the world farmers adopt technologies because they are economic and are positive to their pockets and seldom because they are environmentally friendly. Therefore an economic evaluation of the system under the different agroecologic and socio-economic conditions is essential to have better arguments for adoption. Of course it is misleading to analyze the results of only one or two cropping seasons. Instead an evaluation of the whole system with all its components has to be made, putting value to timeliness, longer life of tractors and less repair costs in this system, improvement of soil fertility, reduced costs for fertilizers and pesticides, the environmental benefits of the system, etc. Thorough economic studies with a system approach have been made by Sorrenson and Montoya (1984) in Brazil and again by Sorrenson et al., (1997 and 1998) in Paraguay. The economic evaluation in 1998 in Paraguay was made on small farms of generally less than 20 ha without tractor mechanization. The study concludes that the total economic benefits arising from adoption of the no-tillage technique on 480.000 ha in Paraguay have been calculated to be US$ 941 million (Sorrenson, 1998). The same author claims that "no other farming techniques have been shown to have such a high impact on farmers incomes, reduce their production costs and risks, and at the same time be environmentally sustainable and generate very considerable net social gains to society" Steps in no-tillage
adoption There are some critical factors that should be considered before starting no-tillage. Therefore we recommend the following to farmers:
Erosion control, improvement of chemical, physical and biological soil conditions, lower machinery costs, reduced labor and tractor hours, timelines, higher economic returns and other benefits of the system will guarantee a steady growth of permanent no-tillage in most regions of the world. Summary The historical development of no-tillage crop production and the successful application in mechanized farms in Latin America, has been closely related to: the availability of appropriate knowledge under different agro-ecological and socio-economic conditions; the availability of a variety of efficient low-cost herbicides; the availability of appropriate machines at adequate prices; the practice of adequate crop rotations including green manure cover crops and most important, a mental change of farmers, technicians, extensionists and researchers away from soil degrading tillage operations to a truly sustainable production system in agriculture. The practice of adequate crop rotations
including green manure cover crops is probably the main factor of successful and
widespread adoption of the technology in many regions of Latin America. Experience has
shown that green manure cover crops do not cost, they will pay. The study of the economic
implication of these practices has shown, that economic returns of no-tillage could be
substantially increased by the use of crop rotations and green manure cover crops. Baker, C.J., Saxton, K.E. and Ritchie, W.R., 1996: No-tillage Seeding, Science and Practice. CAB International, Wallingford, Oxon, UK, 158 pp Calegari, A., Mondardo, A., Bulisani, E.A., Wildner, L.do P., Costa, M.B.B., Alcantara, P.B., Miyasaka, S. e Amado, T.J.C. 1992: Adubação verde no sul do Brasil, AS-PTA, Rio de Janeiro, 346 p. Crovetto, C., 1996. Stubble over the soil. The vital role of plant residue in soil management to improve soil quality. American Society of Agronomy, 238 pp. Derpsch, R. e Calegari, A., 1985: Guia de plantas para adubaçao verde de inverno. IAPAR, Londrina, Documentos 9, Maio de 1985, 96 p. Derpsch, R., 1998: Historical review of no-tillage cultivation of crops. Proceedings, First JIRCAS Seminar on soybean research, March 5 - 6, 1998, Foz do Iguaçu, Brazil, JIRCAS Working Report N° 13, p 1 - 18. Derpsch, R., Roth, C.H., Sidiras, N. and Köpke, U., 1991. Controle da erosão no Paraná, Brasil: Sistemas de cobertura do solo, plantio direto e preparo conservacionista do solo. GTZ, Eschborn, SP 245. Fundação ABC, 1996: Tecnologia de aplicação de defensivo. Fundação ABC para Assistencia e Divulgação Técnica Agropecuária, Castro, PR, Brazil, 36 pp Gazziero, D. L. P., 1998: Control of weeds in no-tillage cultivation. Proceedings, First JIRCAS Seminar on soybean research, March 5 - 6, 1998, Foz do Iguaçu, Brazil, JIRCAS Working Report N° 13, p 43 52 GTZ, 1998: Conserving Natural Resources and Enhancing Food Security by Adopting No-tillage. An Assessment of the Potential for Soil-conserving Production systems in Various Agro-ecological Zones of Africa. GTZ Eschborn, Tropical Ecology Support Program, TÖB publication number: TÖB F-5/e, 53 pp IAPAR, 1981: Plantio direto no estado do Paraná. Fundação Instituto Agronomico do Paraná, Circular N° 23, 244 pp Kelly, H. W., 1983: Keeping the land alive. Soil erosion, its causes and cures. FAO Soils Bulletin N° 50, FAO, Rome. 78 pp Kliewer, I., Casaccia, J., Vallejos, F., 1998: Viabilidade da redução do uso de herbicidas e custos no controle de plantas daninhas nas culturas de trigo e soja no sistema de plantio direto, através do emprego de adubos verdes de curto período. Resumo de Palestras: I Seminário Nacional Sobre Manejo e Controle de Plantas Daninhas em Plantio Direto, 10 12. 8. 1998, Passo Fundo, RS, Editora Aldeia Norte, Passo Fundo, 120 - 123 Lorenzi, H., 1994: Manual de identificação e controle de plantas daninhas, plantio direto e convencional, 4ª edição, Editora Plantarum, Nova Odessa, Brazil, 299 pp Monegat, C., 1991: Plantas de cobertura do solo. Características e manejo em pequenas propriedades. Chapecó (SC). Ed. do Autor, 336 p. Panigatti, J.L., Marelli, H., Buschiazzo, D., Gil, R., (Editors), 1998,: Siembra Directa. INTA - Editorial Hemisferio Sur, Buenos Aires, 333 pp Revista Plantio Direto, 1999 É preciso descompactar o solo?, Revista Plantio Direto Janeiro/Fevereiro de 1999, p 16 - 19. Rodrigues, B.N., Almeida, F.S., e 1998: Guia de herbicidas. 4ª Edição, Editora dos autores, Londrina 1998, 648 pp Ruedell, J., 1990: Efeito do manejo do solo e da rotação de culturas sobre a população de plantas daninhas e na produtividade das culturas. In: Primeras Jorandas Nacionales de Cero Labranza. Concepcion, Sociedad de Conservacion de Suelos de Chile, p. 169-182 Sorrenson, W.J., Montoya, L.J., 1984: Implicações econômicas da erosão do solo e de práticas conservacionistas no Paraná, Brasil, IAPAR, Londrina, GTZ, Eschborn ( no publicado), 231 p. Sorrenson, W.J., López Portillo, J., Nuñez, M., 1997: Economics of No-tillage and crop rotations policy and investment implications, FAO Report N° 97/075/ ISP-PAR, 1 October 1997, Sorrenson, W.J., Duarte, C., López Portillo, J., 1998: Economics of No-till compared to conventional cultivation systems on small farms in Paraguay, policy and investment implications., Report Soil Conservation Project MAG GTZ, August 1998 Warren, 1983: Technology transfer in no-tillage crop production in the third world agriculture. In: No-tillage crop production in the tropics. Proc. Symp., Monrovia, Liberia Published by Int. Plant. Prot. Center, Oregon State Univ., Corvallis, OR, 25-31. Published 2001: D.E. Stott, R.H. Mohtar and G.C. Steinhardt (eds).
Sustaining the Global Farm - Selected Papers from the 10th International Soil
Conservation Organization Meeting held May 24- 29, 1999 at Purdue University
and the USDS- ARS National Soil Erosion Research Laboratory, 248- 254.
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