Abstract

Nitrogen fertilization ensures productivity and persistency of pastures, but may be expensive. Perennial forage peanut, becomes an interesting alternative for N supply. Little is known about its use under grazing. The objective of this study was to evaluate regrowth process of forage peanut using an experimental protocol analogous to tropical forage grasses under rotational grazing. Treatments corresponded to two pre- (95% and maximum canopy light interception – LI95% and LIMax) and two post-grazing (post-grazing heights of 40 and 60% of pre-grazing height) conditions, in a 2x2 factorial arrangement in a randomized complete block design (n = 4). Targets of LI pre-grazing affected pre-grazing height and LI post-grazing. The residual sward LAI did not vary, resulting in similar grazing interval. Greater rates and total herbage accumulation were recorded for LIMax target, consequence of the greater accumulation of stolons at the lower strata of the swards. Greater percentage of leaflets was recorded for the LI95% target. Given the stoloniferous growth habit of forage peanut, stolon accumulation in the lower strata of the sward do not represent a limitation to leaf accumulation and morphological composition. The greater pre-grazing sward height associated with the LIMax target facilitate herbage prehension and intake, further investigation is needed.

Highlights

  • Nitrogen is the most important nutrient for plant development

  • Post-grazing light interception (LI) varied with post-grazing height, with greater values observed for 60% post-grazing heights, as compared to 40% postgrazing height (65.0 and 70.7 ± 0.07% for 40 and 60% post-grazing heights, respectively)

  • Pre-grazing, sward height did not differ between post-grazing heights, when paddocks were managed with LI95%

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Summary

Introduction

Nitrogen is the most important nutrient for plant development. This nutrient integrates essential nucleic acids, amino acids, and the chlorophyll molecule (Stitt & Krapp, 1999). 395-404, Oct-Dec., 2016 greenhouse gas emissions, loss of biodiversity (Schulze et al, 2009; Stoate et al, 2009), contamination and eutrophication of lakes and groundwater (Di & Cameron, 2002). In this context, the use of legumes arises as an alternative to increase N supply, via biological N2 fixation, which represents a sustainable N addition to production systems. Legumes are high in N content and digestibility, and can increase nutritional value of the consumed forage (Barcellos, Ramos, Vilela, Junior, & Bueno, 2008), potentially resulting in increased animal performance and system productivity (Euclides, Macedo, & Oliveira, 1998)

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