Artigo cobre x milho traduzido final
Transcrição
Artigo cobre x milho traduzido final
Development and yield of the maize in response to foliar fertilization with copper ROGÉRIO HIDALGO BARBOSA1; LUCIANE ALMERI TABALDI2*; FÁBIO RODRIGO MIYAZAKI1; MÁRCIO PILECCO3; SAMIR OLIVEIRA KASSAB4; DAÍSA BIGATON5 1 Curso de Agronomia, Faculdade Anhanguera Educacional SA. Rua Manoel Santiago, 1155, Vila São Luís, 79825-150, Dourados – MS. 2 Faculdade de Ciências Agrárias (FCA), Universidade Federal da Grande Dourados - UFGD – Rodovia Dourados - Itahum, Km 12, Caixa Postal 533, Cidade Universitária, 79804-970, Dourados/MS 3 Programa de Pós-Graduação em Zootecnia, FCA/UFGD - Rodovia Dourados - Itahum, Km 12, Caixa Postal 533, Cidade Universitária, 79804-970, Dourados/MS 4 Faculdade de Ciências Biológicas e Ambientais (FCBA), UFGD – Rodovia Dourados - Itahum, Km 12, Caixa Postal 533, Cidade Universitária, 79804-970, Dourados/MS 5 Programa de Pós-Graduação em Agronomia, FCA/UFGD - Rodovia Dourados - Itahum, Km 12, Caixa Postal 533, Cidade Universitária, 79804-970, Dourados/MS Maize under foliar fertilization with copper Palavras-chave: Adubação, Micronutriente, Toxicidade, Zea mays. Section of the article: Agrarian Science *Correspondence to: Drª Luciane Almeri Tabaldi Faculdade de Ciências Agrárias (FCA), Universidade Federal da Grande Dourados - UFGD – Rodovia Dourados - Itahum, Km 12, Caixa Postal 533, Cidade Universitária, 79804-970, Dourados/MS. E-mail: [email protected] ABSTRACT Soil applications of copper may not be effective under particular conditions of soil and climate. Thus, the aim of this study was to evaluate the effects of foliar application of copper on development and yield of DG-501 maize. The experiment was conducted between December 2009 and April 2010, in conventional tillage. When plants were with six to eight leaves, copper (0, 100, 200, 300, 400, 500 and 600g ha-1) was applied to the leaves. Treatments were arranged in randomized complete block, with five replications. When 50% of plants were in flowering, were evaluated the plant height, culms diameter, height of the first ear insertion, leaf area and chlorophyll content. At harvest, it was evaluated diameter and length of ear, yield and thousand grain weight. There was linear reduction in the plants height and in the height of the first ear insertion with increasing copper doses. On the other hand, the chlorophyll content, leaf area, diameter and length of ear, thousand grain weight and yield increased at low doses and decreased at higher copper doses. Therefore, to achieve increase in maize yield without detrimental effects on development, copper can be applied to the leaves in doses not exceeding 100g ha-1. Key words: Fertilization, Micronutrient, Toxicity, Zea mays. INTRODUCTION Maize (Zea mays L.) constitutes one of the main products of Brazilian agriculture, not only in quantitative parameter but also in respect of its strategic significance, being the basis for animal feed. Maize crop has a high yield potential (Gonçalves Jr. et al. 2008). According to the Organization of Nations for Food and Agriculture (FAO), the production of maize in the 2010/2011 crop should reach at 845 million tons, this number probably will be a world record (FAO 2010). However, these yields are low, and are usually irregular (Palhares 2003). It is considered that deficiencies in soil fertility may be listed as one of the main factors responsible for the inability of maize cultivars manifest their full potential genetic production (Ferreira et al. 2001; Carvalho et al. 2004). It is known that the Cerrado soils are weathered and highly acidic, and that they contain small amounts of nutrients that are essential for the cultivation of plants (Vendrame et al. 2010). Moreover, in agreement with previous studies, micronutrient deficiencies in Brazil have been presented more frequently in Cerrado soils (Luchese et al. 2004). Accordingly, several studies are being directed to the use of micronutrients as way of increasing the efficiency of production of plants and improve the economic returns to producers (Alam and Raza 2001). Though required in small quantities by maize plants (Leite et al. 2003), copper (Cu) is essential to complete its life cycle, and when provided in quantities below the requirements, may to occur a decrease in yield (Luchese et al. 2004). Furthermore, Cu occurs in enzymatic compositions of vital importance in plant metabolism, participates in the photosynthesis, respiration, carbohydrate metabolism, nitrogen reduction and fixation, protein metabolism and cell wall (Demirevska-kepova et al. 2004), and in plant resistance to disease (Tomazela et al. 2006). On the other hand, Cu in high concentrations may play roles cytotoxic, inducing stress, altering membrane permeability, protein synthesis and activity of enzymes, causing leaf yellowing and growth retardation (Lewis et al. 2001; Vinit-Dunand et al. 2002). The providing of Cu to crops can be made directly into the soil, in the form of fertilizer; in the plant via foliar fertilizer, or seed treatment (Luchese et al. 2004). Research done by Galrão (1988, 1989) revealed that in field work with broadcast application of 2kg Cu ha-1, in red-yellow oxisol, there was an increase in grain yields for wheat and soybeans crops. Moreover, Cu application in maize seeds in doses of 1 to 6g kg-1 of seeds decreased the ability of seed emergency, without affecting the dry weight of plants that emerged (Luchese et al. 2004). In soil, more than 98% of the Cu of the solution is complexed as chelated with organic compounds of low molecular weight (Faquin 1997). Besides, its greater availability is in the range of pH 5.0 to 6.5. In view of these factors, soil applications may not be effective under particular conditions of soil and climate, for example, high organic matter content or hot and humid summer. In these cases, foliar application of Cu can avoid these problems. With the need of an increase in agricultural yield, is essential the advance in studies of nutritional requirements of different cultures and how nutrients are available to plants. Under certain circumstances, a slight increase in the levels of certain nutrient can cause a significant increase in crop yield. In that sense, for that occur an increase in maize yield is important that studies show the nutritional real needs of that crop for each region, as well as their responses to fertilization levels and the way in which nutrients are available. Thus, the aim of this study was to evaluate the effect of foliar application of different doses of copper (Cu) on development and yield of maize. MATERIAL AND METHODS The experiment was carried out at the Farm School of Faculdade Anhanguera Educacional SA., in Dourados, MS, Brazil, located at 22º13’15”S of latitude, 54º48’21”W of longitude and 430 m of altitude, from December 2009 to April 2010. The climate of Dourados, according to Köppen (1948) is mesothermal humid, Cwa type, with temperature and annual rainfall averages ranging from 20º to 24ºC and 1250-1500mm, respectively. Soil from the cultivated area is classified as dystrophic red oxisol of clayey texture, with the following chemical characteristics: 5.0 of pH in H2O; 25.09g dm-3 organic matter; 36.0mg dm-3 P; 0.0; 24.0; 46.0; 22.0; 53.0; 71.5 and 124.5mmolc dm-3 of Al+3, K, Ca, Mg, H+Al, SB and CTC, respectively; 16.0; 2.1; 13.50 and 22.20mg dm-3 of Fe, Cu, Zn and Mn, respectively, and 57.0% of saturation. Accumulation of rainfall during the execution of the experiment was 603 mm and the average temperature of 25.3ºC (Max. 31.1ºC and Min. 18.7°C). It was used seeds of triple hybrid maize DG-501 of early maturity, with characteristics of grain semi-hard, yellow-orange and medium-sized plants. The seeds were sown in rows in conventional tillage system after soil preparation. Seeds were treated with the imidacloprid (52.5g ha-1) + thiodicarb (157.5g ha-1) insecticides and sown at a depth of 5 to 7cm, spaced 0.90m between rows and five plants per linear meter, corresponding to approximately 55,000 plants per hectare. Fertilization was applied at planting with 500kg per hectare of N-P-K with the formulation 08-10-10, respectively. Control of weeds and defoliating caterpillars was carried out 20 days after sowing (DAS) using a backpack pump of 20L, adjusted to 150L ha-1, using the tembotrione herbicide (100.8g ha-1) and the thiodicarb insecticide (120g ha-1). Treatments were seven increasing doses of copper (0, 100, 200, 300, 400, 500 and 600g ha-1), by foliar application, distributed in a randomized complete block design with five replications of 4 x 5m each (20m2). Pentahydrate sulfate copper (CuSO4.5H2O) (25% Cu) was used as copper source. The spraying was done when the maize plants were with six to eight leaves fully developed, using backpack sprayer with steady flow, equipped with bar 1m, with two nozzles spaced at 0.40m. It was used the spray tip of flat fan TeeJet XR11002, by applying 150L ha-1 of spray. Application was done by keeping the tips at 0.30m height, approximate, above the top of the plant canopy. When 50% of plants were in the flowering period, were evaluated at four plants per plot, the plant height (using a tape line from the soil until insertion of the last leaf); the stem diameter (measured with a digital caliper at 15cm soil) and the height of the first ear insertion (using a tape line, measured of the base from the soil to insertion of the first ear); and chlorophyll content (with Falker Clorofilog). After physiological maturity, at the time of harvest, it was evaluated the diameter and length of the ear (with a caliper on four ears per plot), the yield and thousand grain weight (using ears harvested at three meters central to the plot, ignoring one meter from each side). At harvest, the grains had moisture between 1315%. Data were subjected to analysis of variance and when significance was found by F test, data were subjected to regression analysis by 5% probability. RESULTS AND DISCUSSION The plant height is an indirect method for assessing crop performance (Tittonell et al. 2005). With increasing doses of copper (Cu) there was a linear reduction in the height of maize plants and at the height of the first ear insertion (Fig. 1a and 1b). Genetic studies have shown that these two characteristics show a high correlation with one another (Yan et al. 2010). The reduction in height is a factor that may contribute to the availability of assimilates for grains filling and may when significant, affect yield. On the other hand, studies have shown that smaller plants do not necessarily affect yield, especially in the absence of water stress (Fortin and Pierce 1990). Figure 1 It was suggested that the primary sites of growth inhibition by Cu are molecules of chlorophyll of the pigment antenna of photosystem II (Liddon et al. 1993). Even without the significant effect of Cu on the culms diameter (data not shown), shortening of internodes in maize plants exposed to Cu may compromise the potential of this extra source of photoassimilates located in the culms of the maize plant. This data contradict those reported by Leite et al. (2003), who found that fertilization with Cu ranging from 0 to 16mg kg-1 soil increased significantly the dry weight of shoots of maize plants grown in pots. According Malavolta (2006), Cu concentrations in the experimental area were relatively high (2.1mg dm3 ), suggesting high levels of organic carbon, since organic matter is a major source of this nutrient in soil (Teixeira et al. 2003), explaining, probably, the lack of more significant effects of Cu in maize plants. On the other hand, the relative chlorophyll content and leaf area increased at low doses and decreased at higher doses of copper (Fig. 2). Relative chlorophyll content and leaf area showed maximum points at doses of 257.7 and 112.8g ha-1 of Cu, respectively (Fig. 2a and 2b). This increase in leaf area and chlorophyll content at low doses of Cu can maximize the photosynthetic efficiency of maize plants, mainly by improving the interception of PAR, for more efficient conversion of intercepted radiation into dry matter and photoassimilate partition in the reproductive organs, resulting in higher yield. On the other hand, as the leaf is the main source of assimilates to plant maize (Magalhães et al. 1995), the reduction in leaf area and chlorophyll content in high doses of Cu suggests that the photosynthesis of maize plants may have been harmed due to the adverse effects of Cu on chlorophyll molecule. These data show the toxic effects of Cu at high concentrations, affecting the development and grain production. Figure 2 The same way as for leaf area and chlorophyll content, the data of diameter and ear length (Fig. 2a and 2b, respectively), and thousand grain weight and yield (Fig. 3a and 3b, respectively) showed quadratic response in function of Cu doses, where there was an increase in low doses, with reduction at higher doses. Ear diameter and length had maximum points at doses of 33.87 and 147.44g ha-1 Cu, respectively (Fig. 3a and 3b). Moreover, the points of maximum for thousand grain weight and yield were at doses of 58.26 and 144.29g ha-1 Cu, respectively (Fig. 4a and 4b). At the dose of 144.29g ha-1, Cu provided an increase of 8% in the maize yield (Fig. 4b). Figure 3 These results are related to the data of leaf area and chlorophyll content, indicating that at low doses, Cu promotes an increase in growth and consequently on the yield of maize, the opposite happening in high doses, when the Cu becomes toxic to culture. Luchese et al. (2004) observed symptoms of toxicity in treatments with application of copper equal or greater than 4g kg-1 seed. Figure 4 These data suggest that the reduction in plant height of maize (Fig. 1a) at low doses of Cu did not significantly affect the final yield in these plants, the same did not happening in higher doses of Cu, where a decrease in parameters related to yield was observed. This reduction may be related to the fact that excess Cu inhibits cell elongation, a complex process dependent on cell turgor pressure, synthesis of wall components and growth regulators (Alaoui-Sossé et al. 2004). CONCLUSION Under conditions that the experiment was carried out, it was possible to conclude that to achieve increased yield in maize without detrimental effects on development, the copper can be applied to the leaves in low doses, not exceeding 100g ha-1. REFERENCES ALAM SM AND RAZA S. 2001. Micronutrient Fertilizers. PJBS 4: 1446-1450. ALAOUI-SOSSE B, GENET P, VINIT-DUNAND F, TOUSSAINT M-L, EPRON D, BADOT P-M. 2004. Effect of copper on growth in cucumber plants (Cucumis sativus) and its relationships with carbohydrate accumulation and changes in ion contents. Plant Sci 166: 1213–1218. CARVALHO MAC, SORATTO RP, ATHAYDE MLF, ARF O AND EUSTÁQUIO de SÁ M. 2004. Produtividade do milho em sucessão a adubos verdes no sistema de plantio direto e convencional. PAB 39: 47-53. DEMIREVSKA-KEPOVA K, SIMOVA-STOILOVA L, STOYANOVA Z, HOLZER R AND FELLER U. 2004. Biochemical changes in barely plants after excessive supply of copper and manganese. Environ Exp Bot 52: 253-266. FAO. 2010. Organização das Nações Unidas para Agricultura e alimentação. Available in: https://www.fao.org.br. Access in: 24 September 2010. FAQUIM V. 1997. Nutrição mineral de plantas. Lavras: UFLA/FAEPE, 227 p. FERREIRA ACB, ARAÚJO GAA, PEREIRA PRG AND CARDOSO AA. 2001. Características agronômicas e nutricionais do milho adubado com nitrogênio, molibdênio e zinco. Sci Agric 58: 131-138. FORTIN M-C AND PIERCE FJ. 1990. Developmental and growth effects of crop residues on corn. Agron J 82: 710-715. GALRÃO EZ. 1988. Resposta do trigo à aplicação de cobre em um latossolo orgânico de várzea. Rev Bras Cienc Solo 12: 275-279. GALRÃO EZ. 1989. Efeito de micronutrientes e do cobalto na produção da soja em solo de cerrado. Rev Bras Cienc Solo 13: 41-44. GONÇALVES JR AC, NACKE H, STREY L, SCHWANTES D AND SELZLEIN C. 2008. Produtividade e componentes de produção do milho adubado com Cu e NPK em um argissolo. Sci Agr 9: 35-40. KÖPPEN W. 1948. Climatologia: con un estudio de los climas de la tierra. México: Fondo de Cultura Econômica, 479 p. LEITE UT, AQUINO BF, ROCHA RNC AND SILVA J. 2003. Níveis críticos foliares de boro, cobre, manganês e zinco em milho. Biosc J 19: 115-125. LEWIS S, DONKIN ME AND DEPLEDGE MH. 2001. Hsp70 expression in Enteromorpha intestinalis (Chlorophyta) exposed to environmental stressors. Aquatic Toxicol 51: 277-291. LIDON FC, RAMALHO JC AND HENRIQUES FS. 1993. Copper inhibition of rice photosynthesis. J Plant Physiol 142: 12-17. LUCHESE AV, CONÇALVES-JUNIOR AC, LUCHESE EB AND BRACCINI MCL. 2004. Emergência e absorção de cobre por plantas de milho (Zea mays) em resposta ao tratamento de sementes com cobre. Cienc Rural 34: 1949-1952. MAGALHÃES PC, DURÃES FOM AND PAIVA E. 1995. Fisiologia da planta de milho. Sete Lagoas, Circular Técnica, n. 20. EMBRAPA-CNPMS, 27 p. MALAVOLTA E. 2006. Manual de nutrição mineral de plantas. São Paulo: Ceres. 638 p. PALHARES M. 2003. Distribuição e população de plantas e produtividade de grãos de milho. Piracicaba, 107f. Dissertação (Mestrado em Agronomia - Fitotecnia) – Escola Superior de Agricultura Luiz de Queiroz, Universidade de São Paulo. TEIXEIRA IR, DE SOUZA CM, BORÉM A AND DA SILVA GF. 2003. Variação dos valores de pH e dos teores de carbono orgânico, cobre, manganês, zinco e ferro em profundidade em argissolo vermelho-amarelo, sob diferentes sistemas de preparo de solo. Bragantia 62: 119-126. TITTONELL P, VANLAUWE B, LEFFELAAR PA AND GILLER KE. 2005. Estimating yields of tropical maize genotypes from non-destructive, on-farm plant morphological measurements. Agr Ecosyst Environ 105: 213-220. TOMAZELA AL, FAVARIN JL, FANCELLI AL, MARTIN TN, NETO DD AND DOS REIS AR. 2006. Doses de nitrogênio e fontes de Cu e Mn suplementar sobre a severidade da ferrugem e atributos morfológicos do milho. Rev Bras Milho Sorgo 5: 192-201. VENDRAME PRS, BRITO OR, GUIMARÃES MF, MARTINS ES AND BECQUER T. 2010. Fertility and acidity status of latossolos (oxisols) under pasture in the Brazilian Cerrado. An Acad Bras Cienc 82(4): 1085-1094. VINIT-DUNAND F, EPRON D, ALAOUI-SOSSÉ B AND BADOT PM. 2002. Effects of copper on growth and on photosynthesis in cucumber plants. Plant Sci 163: 53-58. YAN et al. 2010. Stability of QTL across environments and QTL-by-Environment Interactions for Plant and Ear Height in Maize. Agricult Sci China 9: 1400-1412. RESUMO Aplicações de cobre (Cu) no solo podem não ser efetivos sob condições particulares de solo e clima. Assim, o objetivo deste trabalho foi avaliar os efeitos da fertilização foliar com Cu sobre o desenvolvimento e produtividade do milho híbrido triplo DG-501. O experimento foi desenvolvido no período entre dezembro de 2009 e abril de 2010, em sistema de plantio convencional. Quando as plantas encontravam-se com 6-8 folhas totalmente desenvolvidas, Cu (0; 100; 200; 300; 400; 500 e 600g ha-1) foi aplicado via foliar. Os tratamentos foram arranjados em delineamento experimental de blocos casualizados, com cinco repetições. Quando 50% das plantas apresentavam-se no período de florescimento, avaliaram-se a altura de plantas, diâmetro de colmo, altura da inserção da primeira espiga, área foliar e teor de clorofila. Na colheita, avaliou-se diâmetro e comprimento da espiga, produtividade e peso de mil grãos. Houve redução linear na altura de plantas de milho e na altura de inserção da primeira espiga com o aumento das doses de Cu. Por outro lado, os dados de índice relativo de clorofila, área foliar, diâmetro e comprimento da espiga, peso de mil grãos e produtividade aumentaram em baixas doses e diminuíram nas doses maiores de Cu. Portanto, para se obter incremento em produtividade sem efeitos prejudiciais no desenvolvimento da cultura do milho, o Cu pode ser aplicado via foliar em doses não excedendo 100g ha-1. Palavras-chave: Adubação, Micronutriente, Toxicidade, Zea mays. LEGENDS OF FIGURES Figure 1. Plant height (a) and height of insertion of the first ear (b) of maize plants submitted to increasing levels of copper to the leaves. Dourados – 2010. Figure 2. Relative content of chlorophyll (a) and leaf area (b) of maize plants submitted to increasing levels of copper to the leaves. Dourados – 2010. Figure 3. Ear diameter (a) and ear length (b) of maize plants submitted to increasing levels of copper to the leaves. Dourados – 2010. Figure 4. Weight of 1000 grains (a) and yield (b) of maize plants submitted to increasing levels of copper to the leaves. Dourados – 2010. Figure 1 (a) (b) Figure 2 (a) (b) Figure 3 (a) (b) Figure 4 (a) (b)
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