CHARACTERIZATION OF DESIGNER BIOCHAR PRODUCED AT DIFFERENT TEMPERATURES AND THEIR EFFECTS ON A LOAMY SAND
By J. Novak, I. Lima, J. Gaskin, C. Steiner, M. Ahmedna, D. Watts, H. Schomberg. 2009
1,013 citations recorded by the source corpus.
View Paper: https://www.semanticscholar.org/paper/82dbebd2d16aa1a25f1da522d3256706a8b3bddd
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Citations in the corpus
- Biochar properties: Transport, fate, and impact (2016, background): “Novak et al. (2009b) studied the effect of biochar type on water retention and found that biochar from poultry litter had no effect on water retention in soils, whereas biochar from switchgrass almost doubled water retention compared with the control sample.”
- Distributed biochar and bioenergy coproduction: a regionally specific case study of environmental benefits and economic impacts (2013, background): “during thermochemical conversion (Gaskin et al., 2008; Novak et al., 2009) and a uniform recovery factor of 80% is assumed for both base and total ash content of the feedstocks across all scenarios.”
- Effects of pyrolysis temperature on soybean stover- and peanut shell-derived biochar properties and TCE adsorption in water. (2012, background): “Biochar is produced by thermal decomposition of biomass under a negligible or limited supply of oxygen (Novak et al., 2009).”
- Biochar from Biomass and Waste (2010, unknown): “Both spectra show significant aliphatic composition [3] at the 25–35 ppm resonance, and for terminal methyl at *15 ppm.”
- Competitive adsorption of selected non-steroidal anti-inflammatory drugs on activated biochars: Experimental and molecular modeling study (2015, background): “The carbon and ash content are governed by the feedstock (livestock manure > plant > wood) [3] and the condensed aromatic carbon (400– 700 C) as well as the fraction of functional groups (250–400 C) are governed by the pyrolysis temperature [4].”
- Biochar physicochemical properties: pyrolysis temperature and feedstock kind effects (2020, background): “Consequently, such a product exhibits potentially lower ion exchange capacity (Novak et al. 2009).”
- Effects of Feedstock and Pyrolysis Temperature on Biochar Adsorption of Ammonium and Nitrate (2014, background): “This is due to greater losses of volatile components at the higher pyrolysis temperatures [20].”