Abstract
High grain yields of upland rice (Oryza sativa L.) can be achieved in no-tillage systems. However, managing nitrogen (N) fertilization for rice in succession to forage grasses is a challenge because forage residues change N cycling and increase microbial immobilization of N, thereby reducing N availability to the subsequent cash crop. In the present study, two field experiments were conducted to determine if applying all or part of the N fertilizer on preceding palisade grass (Urochloa brizantha) and ruzigrass (Urochloa ruziziensis) or their desiccated residues immediately before rice seeding can supply N to the subsequent rice crop. Forage biomass yield (8–16 Mg ha− 1), N accumulation, and N supply to the subsequent upland rice were highest when all of the N fertilizer was applied on forage grasses at 50, 40 or 35 days before rice seeding (DBS), as opposed to the conventional split application at rice seeding and at tillering. On average, the grain yield of upland rice was 54% higher in succession to palisade grass compared with ruzigrass. The grain yield of rice was higher when N was applied to palisade grass at 35 DBS and ruzigrass at 50 DBS, reaching 5.0 Mg ha− 1 and 3.7 Mg ha− 1, respectively. However, applying N to ruzigrass was less effective for increasing upland rice yields since the yields did not differ from the treatments with the conventional split application. Adjusting the time of N application to forage grasses to increase the grain yields of subsequent upland rice is a sustainable alternative that can promote the economic viability of upland rice production.
Highlights
Rice is a staple food for more than half of the global population, and world rice production is approximately 750 Tg per year (Faostat 2019)
In Experiment 1 (E1), compared with the control, palisade grass dry matter was 39% higher when N was applied 50 DBS (11.5 Mg ha- 1) and decreased in the treatments in which N was applied to live forage grasses closer to rice seeding (40 DBS and 35 DBS)
N application to live palisade grass 35 DBS resulted in an increase in yield compared with the treatments where N was applied over forage residues; at the other times of N application (1 DBS and conventional), the yields did not differ from the control (Fig. 2a)
Summary
Rice is a staple food for more than half of the global population, and world rice production is approximately 750 Tg per year (Faostat 2019). The potential emission of greenhouse gases from flooded rice is more than three times higher than from upland crops (Bouman et al 2007; Carlson et al 2017). Upland rice cultivation has lower water consumption requirements and is compatible with current agricultural production practices in subsistence crop systems, with few purchased inputs to high-technology systems needed (Kumar and Ladha 2011; Crusciol et al 2013). Upland rice cultivation has been used to convert raw land to agriculture, to quickly renew degraded pasture in one growing season, and in rotation with soybean [Glycine max (L.) Merr.] in South America (Santos et al 2006; Bouman et al 2007). Upland rice is a cash crop option for cultivation in crop rotation/succession with maize and soybean that avoids the pathogen cycles associated
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