生物炭
化学
碱度
土壤pH值
土壤水分
阳离子交换容量
农学
碱土
环境化学
土壤科学
环境科学
生物
热解
有机化学
作者
L. Wang,Clayton R. Butterly,Yu Wang,H. M. S. K. Herath,Yunguan Xi,Xiyuan Xiao
摘要
Abstract Strongly acidic soil (e.g. p H < 5.0) is detrimental to tea productivity and quality. Wheat, rice and peanut biochar produced at low temperature (max 300 °C) and differing in alkalinity content were incorporated into X uan‐cheng ( U ltisol; initial p H soil/water = 1/2.5 4.12) and Y ing‐tan soil ( U ltisol; initial pH soil/water = 1/2.5 4.75) at 10 and 20 g/kg (w/w) to quantify their liming effect and evaluate their effectiveness for acidity amelioration of tea garden soils. After a 65‐day incubation at 25 °C, biochar application significantly ( P < 0.05) increased soil p H and exchangeable cations and reduced A l saturation of both tea soils. Association of H + ions with biochar and decarboxylation processes was likely to be the main factor neutralizing soil acidity. Further, biochar application reduced acidity production from the N cycle. Significant ( P < 0.05) increases in exchangeable cations and reductions in exchangeable acidity and Al saturation were observed as the rate of biochar increased, but there were no further effects on soil p H . The lack of change in soil p H at the higher biochar rate may be due to the displacement of exchangeable acidity and the high buffering capacity of biochar, thereby retarding a further liming effect. Hence, a significant linear correlation between reduced exchangeable acidity and alkalinity balance was found in biochar‐amended soils ( P < 0.05). Low‐temperature biochar of crop residues is suggested as a potential amendment to ameliorate acidic tea garden soils.
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