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ARS Home » Midwest Area » Madison, Wisconsin » U.S. Dairy Forage Research Center » Environmentally Integrated Dairy Management Research » Research » Publications at this Location » Publication #384678

Research Project: Improving Nutrient Use Efficiency and Mitigating Nutrient and Pathogen Losses from Dairy Production Systems

Location: Environmentally Integrated Dairy Management Research

Title: Litter mass, deposition rate, and decomposition in nitrogen-fertilized or grass-legume grazing systems

Author
item Jaramillo, David
item DUBEUX, JOSE - University Of Florida
item SOLLENBERGER, LYNN - University Of Florida
item MACKOWIAK, CHERYL - University Of Florida
item VENDRAMINI, JOAO - University Of Florida
item DILORENZO, NICOLAS - University Of Florida
item QUEIROZ, LUANA - University Of Florida
item SANTOS, ERICK - University Of Florida
item GARCIA, LIZA - University Of Florida
item RUIZ-MORENO, MARTIN - University Of Florida
item VAN SANTEN, EDZARD - University Of Florida

Submitted to: Crop Science
Publication Type: Peer Reviewed Journal
Publication Acceptance Date: 1/28/2021
Publication Date: 2/2/2021
Citation: Jaramillo, D.M., Dubeux, J., Sollenberger, L., Mackowiak, C., Vendramini, J., Dilorenzo, N., Queiroz, L., Santos, E., Garcia, L., Ruiz-Moreno, M., Van Santen, E. 2021. Litter mass, deposition rate, and decomposition in nitrogen-fertilized or grass-legume grazing systems. Crop Science. https://doi.org/10.1002/csc2.20475.
DOI: https://doi.org/10.1002/csc2.20475

Interpretive Summary: Plant litter deposition and decomposition play important roles in grassland nutrient cycling. The objective was to evaluate plant litter responses and estimate the N returns via plant litter in contrasting grazing systems, since legume inclusion is hypothesized to result in similar quantities of N return compared with N-fertilized grass systems. Systems were (a) N-fertilized bahiagrass (Paspalum notatum Flüggé) during summer with a mixture of N-fertilized cereal rye (Secale cereale L.) and oat (Avena sativa L.) during winter (Grass+N); (b) bahiagrass (no N fertilizer) during summer and a rye–oat–clovers (Trifolium spp.) mixture + N in winter (Grass+Clover); and (c) bahiagrass (no N fertilizer in summer) with strip-planted rhizoma peanut (Arachis glabrata Benth.) during summer with a rye–oat–clovers mixture + N during winter (Grass+CL+RP). Litter mass was greatest for Grass+N during October (4,430 kg organic matter [OM] ha-1) and least for Grass+CL+RP in June (490 kg OM ha-1). Litter N concentrations were greatest in Grass+N (16 g kg-1), with similar N concentration for Grass+Clover and Grass+CL+RP litter (14 g kg-1). Contribution of C3 species to litter mass increased from May to July but decreased thereafter. Overall, there was a net return of 47 kg N ha-1 yr-1 via litter across the three systems, and litter decomposition was similar in the three systems. Inclusion of forage legumes during cool and warm seasons in grazing systems has the potential to return similar amounts of N through plant litter deposition as grasses receiving moderate levels of N fertilizer.

Technical Abstract: Plant litter deposition and decomposition play important roles in grassland nutrient cycling. The objective was to evaluate plant litter responses and estimate the N returns via plant litter in contrasting grazing systems, since legume inclusion is hypothesized to result in similar quantities of N return compared with N-fertilized grass systems. Systems were (a) N-fertilized bahiagrass (Paspalum notatum Flüggé) during summer with a mixture of N-fertilized cereal rye (Secale cereale L.) and oat (Avena sativa L.) during winter (Grass+N); (b) bahiagrass (no N fertilizer) during summer and a rye–oat–clovers (Trifolium spp.) mixture + N in winter (Grass+Clover); and (c) bahiagrass (no N fertilizer in summer) with strip-planted rhizoma peanut (Arachis glabrata Benth.) during summer with a rye–oat–clovers mixture + N during winter (Grass+CL+RP). Litter mass was greatest for Grass+N during October (4,430 kg organic matter [OM] ha-1) and least for Grass+CL+RP in June (490 kg OM ha-1). Litter N concentrations were greatest in Grass+N (16 g kg-1), with similar N concentration for Grass+Clover and Grass+CL+RP litter (14 g kg-1). Contribution of C3 species to litter mass increased from May to July but decreased thereafter. Overall, there was a net return of 47 kg N ha-1 yr-1 via litter across the three systems, and litter decomposition was similar in the three systems. Inclusion of forage legumes during cool and warm seasons in grazing systems has the potential to return similar amounts of N through plant litter deposition as grasses receiving moderate levels of N fertilizer.