search
for
 About Bioline  All Journals  Testimonials  Membership  News


Archivos Latinoamericanos de Produccion Animal
Asociacion Latinoamericana de Produccion Animal
ISSN: 1022-1301 EISSN: 2075-8359
Vol. 13, Num. 1, 2005, pp. 13-18

Archivos Latinoamericanos de Produccion Animal, Vol. 13, No. 1, Enero-Abril, 2005, pp. 13-18

Effect of defoliation frequencies on the dry matter yield and nutrientcontent of two Centrosema species.

Efecto de la frecuencia de defoliación en la producción de materiaseca y contenido de nutrientes de dos especies de Centrosema

J. Faría-Mármo, D. E. Morillo2nd Z. Chirinosl

La Universidad del Zulia, Departamento de Zootecnia, Postgrado en Producción Animal,
Apartado Postal 526. Maracaibo, Venezuela
2Instituto Nacional de Investigaciones Agrícolas (INIA), Maracaibo, Venezuela.

Recibido Abril 15, 2004.
Aceptado: Enero 18, 2005.

Code Number: la05002

ABSTRACT

A trial was conducted to study the effect of three defoliation frequencies, at F1=4, F2=6 and F3=8 -wk intervals, on dry matter yield (DMY), crude protein (CP) and mineral composition of Centrosema macrocarpum Cm and Centrosema pubescens Cp. A split-plot experimental design with species (main plots), defoliation frequencies (subplots) and three replications was used. Samples for each defoliation frequency, corresponding to rainy (RS) and dry periods (DS), were analyzed for CP and calcium (Ca), phosphorus (P), magnesium (Mg), potassium (K), copper (Cu), iron (Fe), and manganese (Mn) concentrations. DMY of Cm (4.4 t ha-1 year-1) was higher (P<0.05) than of Cp (1.5 t ha-1year-1). DMY increased (P<0.05) with increasing cutting interval (F1=2.4, F2=2.5 and F3=3.6 t ha-1), whereas CP, ash, and most mineral concentrations were not affected (P>0.5). Only Ca declined (P<0.05) with increasing plant maturity. Ca and P concentrations were affected by season (P<0.05). In Cm, Ca concentrations during RS (1.27%) were lower than in the DS (1.55%), whereas in Cp, P concentrations were higher (P<0.05) in RS (0.25%) than in DS (0.21%). In both species, Fe, Cu and Mn concentrations decreased (P<0.05) during RS. Other elements were not affected (P>0.05) by season. Mineral concentrations of the two species were adequate to cover grazing ruminant nutritional requirements with the possible exception of P (0.21%). Forage P concentrations may have been influenced by the low soil P content. Ash and Cu concentrations were lower (P<0.005) in Cm than Cp but CP and mineral composition did not differ between species.

Keys words: Centrosema, defoliation frequencies, yield, crude protein, mineral composition.

RESUMEN

Se estudió el efecto de tres frecuencias de defoliación (F) a intervalos de F1=4, F2=6 y F3=8 semanas sobre la producción de materia seca (PMS), proteína bruta (PB), y composición mineral de Centrosema macrocarpum Cmy Centrosema pubescens Cp. Se utilizó un diseño de bloques al azar en parcelas divididas y tres repeticiones, con especies (parcela principal), y las frecuencias de defoliación (parcela dividida). Se analizaron muestras de cada F para PB, Calcio (Ca), fósforo (P), magnesio (Mg), potasio (K), cobre (Cu), hierro (Fe), y manganeso (Mn) durante las épocas seca (ES) y lluviosa (ELL). La PMS fue mayor (P<0,05) para Cm (4,4 t ha1 año -1) que Cp (1,5 t ha-1 año -1). El incremento de F aumentó la PMS (F1=2,4, F2 =2,5 y F3 = 3,6 t ha-1), sin afectar (P>0.05) la PB, ceniza y la mayoría de los minerales; solo Ca disminuyó (P<0,05) con la madurez. En Cm el Ca fue menor (P<0,05) durante ELL (1,27%) que en ES (1,55%), mientras que en Cp el P (0,25%) fue mayor (P<0,05) durante ELL que en ES (0,21%). En ambas especies el Fe, Cu y Mn disminuyeron (P<0,05) durante ELL. Otros elementos no se afectaron (P<0,05) por la época del año. Los minerales de ambas especies resultaron adecuados para rumiantes a pastoreo con la posible excepción del P (0,21%) posiblemente por el bajo P del suelo. La ceniza y el Cu fueron menores (P<0,05) en Cm que en Cp, pero la PB y los restantes minerales no difirieron entre especies.

Palabras claves: Centrosema, frecuencia de defoliación, proteína bruta, composición mineral

INTRODUCTION

Centrosema is a legume genus native to Central and South America, and includes species with potential adaptation to diverse habitats such as the dry and high-altitudes tropics, subtropics, poorly drained and/or seasonally flooded conditions, and acid, low-fertility soils (Schultze-Kraft et al.,1990). Studies have focused on the well-drained isohyperthermic savannas («Llanos» ecosystem) and tropical forest ecosystem of Colombia and Venezuela, where several Centrosema species such as C. macrocarpum and C. pubescens have shown considerable forage potential (Grof et al., 1997).

Centrosema macrocarpum is a promising legume for a wide range of ecological conditions throughout the tropics. Its excellent forage yield, drought tolerance and high nutritive value are considered of particular importance (Miles and Lapointe, 1992).

Centrosema pubescens is the only well-known Centrosema species that has been widely evaluated, is available commercially, and has the largest number of collected germplasm accessions. Some systematic screening has been carried out on noncommercial lines of C. pubescens. Regional reports (CIAT, 1990) show to a varying degree that these accessions have potential for acid soil sites in humid tropical environments, but not in savanna ecosystems. Several studies have been conducted in different ecological areas of Venezuela to evaluate the dry matter yield (DMY) of several accessions of Centrosema pubescens (Faría-Marmol et al.,1997a; Grof et al., 1997; Pirela-León et al., 1997). Among the highest yielding accessions, CIAT (Centro Internacional de Agricultura Tropical) No. 15160, has shown the best performance.

Further research on Centrosema macrocarpum and Centrosema pubescens is needed to assess their forage yield and nutrient concentration in the local environment. The objective of this study was to evaluate the effect of three defoliation frequencies on DMY, crude protein (CP) concentration and mineral composition of Centrosema macrocarpum and Centrosema pubescens during two seasons in a wet/ dry region of Venezuela.

MATERIALS AND METHODS

The experiment was conducted on a farm located in Zulia State, western region of Venezuela (10º 32' 32'' N and 72º 12' 30'' W), with climate and vegetation corresponding to a tropical dry forest. Mean annual rainfall is 960 mm, distributed in a dry (four months) and a rainy (eight months) season. Total precipitation during the experiment (336 days) was 730 mm, distributed between one «dry» (90 mm, 156 days) and one «rainy» (640mm, 180 days) period. Soil was a sandy-loam Typic Haplustalf with pH 5.2 and 2.68% organic matter. Average soil macroelement analysis (mg/kg) was: phosphorus (P), 8; calcium (Ca), 100; potassium (K), 60 and magnesium (Mg), 324.

Two species of Centrosema, C. macrocarpum CIAT 5713 and C. pubescens CIAT 15160 were evaluated in a split-plot experimental design containing three replications, with species as the main plots (36m2) and defoliation frequencies (4, 6, and 8 week-intervals) as the subplots (12 m2).

The available forage 10 cm above the ground in the central 2 x 2-m area of each plot was cut using hand shears, weighed, and a sample (ca. 500 g) consisting of 10 grab sub-samples was taken to determine dry matter concentration at 60 oC for 48 hours, and to estimate DMY.

Dry matter yield was evaluated throughout the whole year. Samples from the first, mid and last cuttings for each frequency in two replications, corresponding to rainy and dry periods, respectively, were used to determine CP concentration by the Kjeldhal (Kjeldhal N x 6.25) procedure (Horwitz,1982). Sub-samples for macro and microelement analyses were processed following the methods outlined by Fick et al. (1979), and P was analyzed by a colorimetric technique (Harris and Popat, 1954). Calcium, K, Mg, Cu, Fe and Mn concentration were determined by flame atomic absorption spectrophotometry (AAS), (Perkin-Elmer Corp, 1982).

Data were subjected to ANOVA for a split plot design using the General Linear Model procedure of SAS (1992). If appropriate, means were compared using Duncan's Multiple Range Test as described by Steel and Torrie (1992).

RESULTS AND DISCUSSION

Mean dry matter yields of C. macrocarpum and C. pubescens as affected by the frequency of defoliation and species are presented in Table 1. The interaction species x frequencies was not significant (P>0.05) for DMY. DMY increased (P<0.05) when the cutting interval was increased from 4 to 8 weeks. Dry matter production was higher (P<0.05) in C. Macrocarpum than in C. pubescens. These results are similar to those reported in areas with low rainfall and a long dry season (CIAT, 1990; Pérez, 1995). Dry matter yields obtained in this research were comparable to those reported in savanna ecosystems but lower than those found in the humid tropics (CIAT, 1990).

DM yield declined (P<0.05) in C. macrocarpum (75.9%) and C. pubescens (85.3%) during the dry season as compared to the wet season. These results are similar to those reported by CIAT (1990), Faría-Mármol (1995) and Faría-Mármol et al. (1997a), and can be ascribed to the effect of water deficit on plant growth and development (Buxton and Fales, 1994).

CP, ash and mineral concentrations for C. macrocarpum and C. pubescens are shown in Table 2. No differences (P>0.05) were detected between species for CP and concentration of most mineral. Only ash and Cu concentrations were lower (P<0.05) in C. macrocarpum than in C. pubescens. All mean and individual concentrations for the macro and trace elements evaluated in this research were below the suggested maximum tolerable levels for cattle (NRC, 1980; McDowell, 1992).

Mean CP concentrations (22 and 18%) were within the range reported for Centrosema spp growing in Venezuela (Pérez, 1995; Faría-Mármol,1995; Faría-Mármol et al., 1997b) and other tropical regions (Shultze-Kraft et al., 1990; Lascano et al., 1990). These values are considerably higher than 7%, which is the minimum CP content indicated by Milford and Minson (1965) to avoid a depression in forage voluntary intake by grazing livestock. The mean ash concentration was consistently below 9.5 % in both species.

Mean Ca, K and Mg concentrations, as well as all the individual values, can be regarded as adequate for ruminant livestock when compared to the mineral element requirement (MER) or critical level for deficiency (McDowell, 1992; NRC, 1989, 1996). Conversely, mean P concentrations, with relative deficiencies of 44 and 78% in Cm and Cp, respectively, are inadequate according to the same reference values.

Mean Ca:P ratios (6.4:1) were within the tolerable range for ruminants (NRC, 1989, 1996). Several investigations (Wise et al., 1963; Ricketts et al., 1970) have demonstrated a significant decrease in growth and feed efficiency of cattle fed dietary Ca:P ratios over 7:1. For both Centrosema species, mean Fe and Mn concentrations as well as all the individual values of these elements, are considered adequate according to the MER suggested for ruminants (McDowell, 1992; NRC 1989, 1996). However, differences (P<0.05) between forage species were detected for Cu concentrations. Cu concentrations, which were adequate in Cp in relation to the suggested requirement for grazing ruminants, but marginal in Cm with 44% of the individual values below the critical level for deficiency.

The effect of defoliation frequencies on nutrient concentrations of C. macrocarpum and C. pubescens are presented in Table 3. All nutrients evaluated in this study tended to decrease with increasing forage maturity, no differences (P>0.05) among cutting frequencies were observed for ash and most minerals. Only Ca concentrations declined (P<0.05) with increasing plant maturity. The lowest Ca concentration (1.1%) was obtained with the longest cutting interval, probably due to an increase in the proportion of the stem fraction as the forage matures since stems generally contains less Ca than leaves (Minson, 1990). A general declining trend with increasing plant maturity has been reported for Ca, P, K and microelements concentrations by some researchers (Underwood, 1981; Spears, 1994), whereas Minson (1990) pointed out that except for Cu, which usually follows the general trend, plant age has had conflicting or inconsistent effects on mineral concentrations.

Seasonal means for CP, ash and mineral concentrations of two Centrosema species are given in Table 4. Mean PC values were high and similar (P>0.05) for the dry (18.78%) and rainy seasons (20.28%) in both forage species and agree with those reported by Lascano et al. (1990) and Faría-Mármol et al. (1997b).

Calcium concentration of C. macrocarpum was lower (P<0.05) during the rainy season (1.55%) than the dry season (1.27%), whereas no differences (P>0.05) were detected for other macroelement concentrations in that species. Phosphorus was the only macroelement affected (P<0.05) by season in C. pubescens, with a higher value during the rainy season (0.27%) than the dry season (0.22%).

Mean Fe, Cu, and Mn concentrations declined (P<0.05) during the rainy season. Except for Cu, trace mineral concentrations were regarded as adequate in both seasons and in both species. Copper concentration of C. macrocarpum was below the recommended level for ruminants during the dry season. Kabaija and Smith, 1989 reported an unexplained increase in the concentration of Mn, Fe, Zn and Cu during the dry season. Seasonal changes in microelement concentrations of forage have been reported, but there is not consistency in the direction of the changes (Minson, 1990).

CONCLUSIONES

Centrosema macrocarpum produced higher DMY than C. pubescens, and DMY increased with increasing harvest interval. However, crude protein, ash and most mineral concentrations were not affected by the frequency of defoliation. Only Ca concentrations decreased with increasing plant maturity. Crude protein concentrations and most mineral nutrients were similar between forage species. From the standpoint of ruminant nutrition, P concentrations in both species and Cu concentration in C. macrocarpum were deficient. Most mineral concentrations were affected by season, but those changes may not be nutritionally significant. The importance of these deficiencies will depend on the amount and composition of other ingredients of the diet, since these species are usually grown in association with grass species.

LITERATURE CITED
  • Buxton, D., R. and S. Fales. 1994. Plant environment and quality. In: G. C. Fahey, Jr. (ed), Forage Quality, Evaluationand Utilization. ASA, CSSA, SSSA, Madison, WI. pp. 155199.
  • CIAT (Centro Internacional de Agricultura Tropical). 1990. Centrosema: Biology, Agronomy, and Utilization. Schultze-Kraft, R. and R. Clemens (tech. eds.). CIAT, Cali. Colombia. 1245 pp.
  • Faría-Mármol, J. 1995. Potencial forrajero de accesiones venezolanas de Centrosema pubescens. Pasturas Tropicales 17:1417.
  • Faría-Mármol, J; I. González, Z. Chirinos y J. R. Faría. 1997a.Producción de materia seca y características de crecimiento de Centrosema pubescens en una región semiárida de Venezuela. Archivos Latinoamericanos de Producción Animal 5 (Suplemento 1):48-50.
  • Faría-Mármol, J., J. R. Faría, I. González y Z. Chirinos. 1997b.Variación estacional de la proteína cruda y digestibilidadin vitro de la materia orgánica en accesiones promisorias deCentrosema pubescens. Archivos Latinoamericanos de Producción Animal. 5 (Suplemento 1): 51-53.
  • Fick, K. R., L. R. Mcdowell, P. Miles, N. Wilkinson, J. D. Funk y J. H. Conrad. 1979. Methods of Mineral Analysis of Plantand Animal Tissues. (Second ed.). Animal ScienceDepartment, University of Florida, Gainesville, FL. 763 pp.
  • Grof, B., A. Flores, P. Mendoza y A. Pizarro. 1997. Experienciaregional con Centrosema: norte de América del Sur. In: R.Shultze-Kraft, R. Clements, y G. Keller- Grein (eds.),Centrosema: Biología, Agronomía y Utilización. CIAT, Cali,Colombia. pp. 455-488.
  • Harris, W. D. y P. Popat. 1954. Determination of thephosphorus content of lipids. Am. Oil Chem. Soc. 31:124
  • 127.
  • Horwitz, W. 1982. Official Methods of Analysis. 12th ed. Association of Official Analytical Chemist, Washington,DC.
  • Kabaija, E. y O. B. Smith, 1989. Influence of season and age ofregrowth on the mineral profile of Gliricidia sepium and Leucaena leucocephala. Trop. Agric. (Trinidad) 66:125-128.
  • Lascano, C. E. J. Teitzel, E. P. Kong. 1990. Nutritive value ofCentrosema and animal production. In: R. Shultze- Kraftand R. J. Clements (tech eds.), Centrosema: biology,agronomy and utilization. CIAT, Cali, Colombia. pp. 271
  • 292.
  • Mcdowell, L. R. 1992. Minerals in Animal and Human Nutrition. Academic Press, Inc. San Diego, CA.
  • Faría-Mármol et al.
  • Miles, J. y S. Lapointe. 1992. Regional germoplasm evaluation:A portfolio of germoplasm options for the major ecosystemsof tropical America. In: CIAT (Centro Internacional deAgricultura Tropical). Pasture for the Tropical Lowlands:CIAT's Contributions. Centro Internacional de AgriculturaTropical, Cali, Colombia. pp. 9-28.
  • Milford, R. y D. J. Minson. 1965. Intake of tropical pasturespecies. In: Proceedings of the 9th International GrasslandCongress, Sao Paulo, Brazil. pp. 815-822.
  • Minson, D. J. 1990. Forage in Ruminant Nutrition. AcademicPress, Inc., San Diego, California.483 p.
  • NRC. (National Research Council). 1980. Mineral Tolerance ofDomestic Animals. National Academy of Sciences, NationalResearch Council, Washington, DC.
  • NRC. (National Research Council). 1989. NutrientRequirements of Domestic Animals. Nutrient Requirementsof Dairy Cattle. Sixth Revised Ed. National Academy ofSciences, National Research Council, Washington, DC.
  • NRC. (National Research Council). 1996. NutrientRequirements of Domestic Animals. Nutrient Requirementsof Beef Cattle. Seventh Revised Ed. National Academy ofSciences, National Research Council, Washington, DC.
  • Pérez, G.1995. Evaluación de la adaptabilidad de especiesforrajeras en la zona de Yaguas, Carora, estado Lara. Universidad del Zulia. Postgrado de Producción Animal. Facultades de Agronomía y Ciencias Veterinarias. Maracaibo,Venezuela. (Tesis de Maestría) 155pp.
  • Perkin-Elmer Corporation. 1982. Analytical Methods forAtomic Absorption Spectrophotometry. Perkin-ElmerCorp., Norwalk, CT.
  • Pirela-León, M. F., D. Morillo y J. Faría-Mármol. 2003. Evaluación de cinco accesiones de Centrosema pubescens para laalimentación de bovinos en un bosque húmedo tropical.Revista Científica, FCV-LUZ / Vol. XII, N o 1, 28-32.
  • Ricketts, R.E., J. R. Campbell, D. Weiman y M. Tumbleson.1970. Effect of three calcium:phosphorus ratios on performance of growing Holstein steers. J. Dairy Sci. 5: 898-903.
  • Schultze-Kraft, R., G. Keller-Grein, J. Belalcazar y G. Benavides.1990. Centrosema macrocarpum Benth, a promising tropicalforage legume for acid soils. In: Proceedings of the XVInternational Grassland Congress, Kyoto. Science Councilof Japan and Japanese Society of Grassland Science, Japan.pp. 152- 154.
  • Spears, J. 1994. Minerals in forages. In: G. C Fahey, Jr et al., (ed), Forage Quality, Evaluation and Utilization. ASA,CSSA, SSSA., Madison, WI. pp. 281-317.
  • Statistical Analysis System (SAS). 1992. Introductory Guidefor Personal Computers. Basics. Statistical Analysis SystemInstitute, Inc., Cary, NC.
  • Steel, R. G. D. y J. H. Torrie. 1989. Bioestadística: Principios yProcedimientos. (Segunda Edición). McGraw-Hill Int.Mexico. 1831 pp.
  • Underwood, E. J. 1981. The Mineral Nutrition of Livestock. 2nd ed. Commonwealth Agricultural Bureau, London,
  • Wise, M. B., A. L. Ordoveza y E. R. Barick. 1963. Influence ofvariations in dietary calcium:phosphorus ratios on performance and blood constituents of calves. J. Nutr. 79:79-84.

 

© 2005 ALPA. Arch. Latinoam. Prod. Anim.


The following images related to this document are available:

Photo images

[la05002t3.jpg] [la05002t4.jpg] [la05002t1.jpg] [la05002t2.jpg]
Home Faq Resources Email Bioline
© Bioline International, 1989 - 2024, Site last up-dated on 01-Sep-2022.
Site created and maintained by the Reference Center on Environmental Information, CRIA, Brazil
System hosted by the Google Cloud Platform, GCP, Brazil