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An investigation of the effect of biochar application rates on CO(2) emissions in soils under upland rice production in southern Guinea Savannah of Nigeria

Biochar is a chemically recalcitrant carbon-rich solid material used in soil for its potential to improve soil quality and sequester carbon. While the rate of application has implications for soil carbon dioxide (CO(2)) emission and the overall benefits of biochar, its effects are yet to be fully un...

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Detalles Bibliográficos
Autores principales: Olaniyan, John Olajide, Isimikalu, Theophilus Olufemi, Raji, Bashiru Ademola, Affinnih, Kehinde Olayemi, Alasinrin, Sikiru Yusuf, Ajala, Olusegun Nathaniel
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Elsevier 2020
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7701194/
https://www.ncbi.nlm.nih.gov/pubmed/33294705
http://dx.doi.org/10.1016/j.heliyon.2020.e05578
Descripción
Sumario:Biochar is a chemically recalcitrant carbon-rich solid material used in soil for its potential to improve soil quality and sequester carbon. While the rate of application has implications for soil carbon dioxide (CO(2)) emission and the overall benefits of biochar, its effects are yet to be fully understood. To evaluate the effect of application rates of rice husk biochar on CO(2) emissions, 91-day field experiments were conducted on three soil types (Anthraquic Ustorthent, Grossarenic Kandiustalf, and Ustic Quartzipsamment) in the southern Guinea Savannah of Nigeria, using three biochar application rates of 5, 15 and 25 t h(−1), and control. A two-way ANOVA showed that cumulative CO(2) emissions were significantly (p < 0.01) different between soil types and treatments, and soil type/treatment interactions were also significant at p = 0.05. The highest cumulative CO(2)–C emission of 2.77g/m(2) was recorded in the Grossarenic Kandiustalf, while the least value of 2.11g/m(2) was recorded in the Ustic Quartzipsamment. CO(2) emission increased with increasing biochar application rates, with the highest (3.06 CO(2)–C g/m(2)) value recorded at 25 t/ha compared to 2.78 g/m(2) and 1.52 g/m(2) values recorded for 5 t/ha and control treatments respectively. While CO(2) emissions increased with biochar application rate however, the percentage of biochar-C mineralized was higher at lower biochar rates, and differences were significant at p = 0.01. While 0.63 % of biochar C was mineralized under 5 t/ha biochar treatment, 0.15 % was recorded for 25 t/ha treatment. Factors that had significant correlation with CO(2)–C emission in the soils were biochar addition rate, soil pH, N, P, Ca, Mg and K. At day 91, there were no significant differences in CO(2) emissions between amended treatments and control, and only a small percentage (<1) of biochar C had been mineralized.