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Effects of Feedstock and Pyrolysis Temperature on Biochar Adsorption of Ammonium and Nitrate
Biochar produced by pyrolysis of biomass can be used to counter nitrogen (N) pollution. The present study investigated the effects of feedstock and temperature on characteristics of biochars and their adsorption ability for ammonium N (NH(4) (+)-N) and nitrate N (NO(3) (−)-N). Twelve biochars were p...
Autores principales: | , , , , , , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
Public Library of Science
2014
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC4254611/ https://www.ncbi.nlm.nih.gov/pubmed/25469875 http://dx.doi.org/10.1371/journal.pone.0113888 |
Sumario: | Biochar produced by pyrolysis of biomass can be used to counter nitrogen (N) pollution. The present study investigated the effects of feedstock and temperature on characteristics of biochars and their adsorption ability for ammonium N (NH(4) (+)-N) and nitrate N (NO(3) (−)-N). Twelve biochars were produced from wheat-straw (W-BC), corn-straw (C-BC) and peanut-shell (P-BC) at pyrolysis temperatures of 400, 500, 600 and 700°C. Biochar physical and chemical properties were determined and the biochars were used for N sorption experiments. The results showed that biochar yield and contents of N, hydrogen and oxygen decreased as pyrolysis temperature increased from 400°C to 700°C, whereas contents of ash, pH and carbon increased with greater pyrolysis temperature. All biochars could sorb substantial amounts of NH(4) (+)-N, and the sorption characteristics were well fitted to the Freundlich isotherm model. The ability of biochars to adsorb NH(4) (+)-N followed: C-BC>P-BC>W-BC, and the adsorption amount decreased with higher pyrolysis temperature. The ability of C-BC to sorb NH(4) (+)-N was the highest because it had the largest cation exchange capacity (CEC) among all biochars (e.g., C-BC400 with a CEC of 38.3 cmol kg(−1) adsorbed 2.3 mg NH(4) (+)-N g(−1) in solutions with 50 mg NH(4) (+) L(−1)). Compared with NH(4) (+)-N, none of NO(3) (−)-N was adsorbed to biochars at different NO(3) (−) concentrations. Instead, some NO(3) (−)-N was even released from the biochar materials. We conclude that biochars can be used under conditions where NH(4) (+)-N (or NH(3)) pollution is a concern, but further research is needed in terms of applying biochars to reduce NO(3) (−)-N pollution. |
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