Characterisation, adsorption and desorption of ammonium and nitrate of biochar derived from different feedstocks

Biochar is known to be a highly adsorptive material, especially when the biochar is altered by activation to further increase its sorption ability. Little information, however, is available on the potential reversibility of both ammonium (NH4+) and nitrate (NO3-) sorption on the inherent biochar pH. The objective of our study was to characterise biochars made using different pyrolysis conditions from five various plant materials and rubber tyre, and to use them to investigate the biochar properties responsible for NH4+ and NO3- adsorption and desorption. The rubber tyre, maize stover and sugarcane pith were the weakest adsorbing biochars (5.77.8 mg g(-1)) and best described by the Freundlich adsorption isotherm. The grape pip, grape skin and pine wood biochars had adsorption capacities in the range 8.3-9.4 mg NH4+ g(-1) and best described by a linear adsorption isotherm at 100 mg L-1. The NH4+ adsorption results were associated with physisorption which implies that they can act as slow release NH4+ fertilisers if NH4+ is bioavailable. The six biochars had NO3- adsorption capacities in the range 15.215.9 mg g(-1) and were well fitted to the linear adsorption isotherm at 100 mg L-1. All six biochars had a stronger NO3- removal affinity (82-89%) compared to NH4+ (33-39%). Adsorbed nitrate was not desorbable (0.01-0.23%) compared to adsorbed NH4+ which was 53-60% desorbable. The desorption result was possibly due to NO3- competing redox reactions or NO3- being too strongly adsorbed for extraction. Desorption of NH4+ was associated with biochar net negative pH values and volatilisation of ammonia.

Automated summary

Biochar is a highly adsorptive material that can be altered by activation to increase its sorption ability. This study investigated the NH4+ and NO3- sorption and desorption properties of biochars made from various plant materials and rubber tyre. The results showed differences in adsorption capacities, desorption rates, and potential implications for slow-release fertilizers and environmental remediation.