2015
DOI: 10.1016/j.soilbio.2015.01.006
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Effects of temperature and processing conditions on biochar chemical properties and their influence on soil C and N transformations

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Cited by 180 publications
(95 citation statements)
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References 88 publications
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“…that degrade lignin in wood waste can enhance the degradation of persistent organic pollutants such as pentachlorophenol (Mileski et al, 1988). Microbial inhibition in biosolids caused by poor aeration, low pH, or high concentrations of metals may be reduced by mixing the biosolids n/g (Paramashivam et al, 2016b), (Wilén et al, 2004) Pine ( (12) 55 (12) (Enders et al, 2012), (Pereira Calvelo et al, 2011), (Hina et al, 2010) n/a n/a n/a n/a (Zhang et al, 2015) 600 9.6 37.1 0.4 n/a n/a 42.6 n/a n/a n/a n/a Lignite New Vale, New Zealand with organic amendments (Song and Schobert, 1996;Pehlivan and Arslan, 2007;Chassapis et al, 2009;Knowles et al, 2011;Simmler et al, 2013;Doskocil et al, 2015). Xenobiotics can be immobilized or entrapped within the micropores of organic soil amendment (Fetzner, 2000).…”
Section: Sorption Of Xenobiotics and Heavy Metalsmentioning
confidence: 99%
“…that degrade lignin in wood waste can enhance the degradation of persistent organic pollutants such as pentachlorophenol (Mileski et al, 1988). Microbial inhibition in biosolids caused by poor aeration, low pH, or high concentrations of metals may be reduced by mixing the biosolids n/g (Paramashivam et al, 2016b), (Wilén et al, 2004) Pine ( (12) 55 (12) (Enders et al, 2012), (Pereira Calvelo et al, 2011), (Hina et al, 2010) n/a n/a n/a n/a (Zhang et al, 2015) 600 9.6 37.1 0.4 n/a n/a 42.6 n/a n/a n/a n/a Lignite New Vale, New Zealand with organic amendments (Song and Schobert, 1996;Pehlivan and Arslan, 2007;Chassapis et al, 2009;Knowles et al, 2011;Simmler et al, 2013;Doskocil et al, 2015). Xenobiotics can be immobilized or entrapped within the micropores of organic soil amendment (Fetzner, 2000).…”
Section: Sorption Of Xenobiotics and Heavy Metalsmentioning
confidence: 99%
“…The overall primary pyrolysis stage is completed at relatively low temperatures, around 500 °C (Neves et al, 2011), and yields a C-rich solid: charcoal or biochar, depending on its use. In general, the higher the temperature, the higher will be the pH, C, mineral and ash content, C stability and biochar aromaticity, porosity, and specific surface area, and the lower will be the volatile content and yield (Wu et al, 2012;Zhao et al, 2013;Zhang et al, 2015b).…”
Section: T E M P E R a T U R E C O N T R O L S B I O M A S S Thermo-dmentioning
confidence: 99%
“…Clough et al (2013) reviewed the studies examining NO 3 − sorption on biochar and concluded that sorption of NO 3 − onto a biochar surface was unlikely to occur unless the pyrolysis temperature during biochar manufacture was >600°C, with the degree of NO 3 − sorption also dependent on feedstock type. Other more recent studies, also showing low sorption of NO 3 − by biochar, have generally examined biochar manufactured at pyrolysis temperatures <600°C (Gai et al, 2014; Hale et al, 2013; Zhang et al, 2015). Chintala et al (2013) showed that NO 3 − sorption of a biochar produced at 650°C was only significant in acidic conditions.…”
Section: Resultsmentioning
confidence: 99%
“…A slow pyrolysis method was used to produce low‐temperature biochars. A muffle furnace was used to manufacture biochars at 350°C in a low‐oxygen environment (Zhang et al, 2015). Sawdust (200 g) was weighed into steel containers covered with aluminum foil.…”
Section: Methodsmentioning
confidence: 99%