132-1 Nitrous Oxide and Ammonia Emissions from N Fertilization of Maize in a Brazilian Midwest Oxisol.

Poster Number 606

See more from this Division: ASA Section: Environmental Quality
See more from this Session: Agricultural Practices to Improve Nitrogen-Use Efficiency and Mitigate Greenhouse Gas Emission: I (includes student competition)

Monday, November 16, 2015
Minneapolis Convention Center, Exhibit Hall BC

Maria da Conceição Santana Carvalho1, Márcio Reis Martins2, Beata Emoke Madari3, Claudia Pozzi Jantalia4, Katharina Plassmann5, Luis Omar Torres Dorante5 and Nelson Horowitz6, (1)Embrapa Rice and Beans, EMBRAPA - Empresa Brasileira de Pesquisa Agropecuaria, Santo Antônio de Goiás, (Non U.S.), BRAZIL
(2)Embrapa Agrobiology, Brazilian Agricultural Research Corporation, Seropédica, RJ, Brazil
(3)Embrapa Rice and Beans, Brazilian Agricultural Research Corporation - Embrapa, Santo Antonio de Goias, Brazil
(4)Embrapa Agrobiology, Brazilian Agricultural Research Corporation - Embrapa, Seropedica, Brazil
(5)Research Centre Hanninghof, Yara International, Duelmen, Germany
(6)Yara Brasil, Yara, Porto Alegre, Brazil
Abstract:
The Brazilian Midwest region is responsible for more than 44% of corn (Zea mays L.) produced in the country. This crop is one of the largest consumers of syntetic N-fertilizers in Brazil, which is an agricultural practice of growing environmental concern as one important source of N2O emission. In a field experiment we quantified N2O emissions and NH3 volatilization from surface-applied fertilizers on maize crop under center pivot in the Brazilian savannah in a clayly Oxisol. We used three fertilizers at the rate of 150 kg N ha-1 splitted into two topdressings-N (40 kg N ha-1 at V1-V2 and 110 kg N ha-1 at V4-V6 growth stage), which were: calcium ammonium nitrate - CAN, urea, and ammonium sulfate, and a control (without N application). The treatments were arranged in a randomized block design with five replications. We found that the greatest N2O emissions were concentrated in the first two weeks after application of fertilizers, with peaks between three and four days. Higher emissions were observed after the second fertilization due to the higher amount applied. The N2O emissions, and particularly the emissions measured in the CAN fertilizer treatment, were clearly related to the N-NO3- availability in soil interacting with the very high water content (WFPS > 60%). The calcium ammonium nitrate showed the highest N2O emission factor (0.84%), followed by urea (0.42%), and ammonium sulfate (0.41%).  Due to strong rainfall events (> 20 mm) less than 24 hours after fertilizer application, the cumulative N loss as volatilized NH3 from urea was very low (2.7%) and significantly higher than ammonium sulfate, and CAN. The results show that at such conditions and production systems, N-fertilizers showed lower N2O emissions than IPCC default emission factor (1%). No significant diferences among fertilizers were found for productivity.

See more from this Division: ASA Section: Environmental Quality
See more from this Session: Agricultural Practices to Improve Nitrogen-Use Efficiency and Mitigate Greenhouse Gas Emission: I (includes student competition)

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