Biochar Alters Inorganic Phosphorus Fractions in Tobacco-growing Soil

It is important to consider tobacco stalks as sources of biochar and improve the soil quality of tobacco-producing areas in Southwest China. Therefore, in this study, we investigated the effects of biochar produced from tobacco stalks on soil inorganic phosphorus (P) fractions in bulk and rhizospher...

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Veröffentlicht in:Journal of soil science and plant nutrition 2021-06, Vol.21 (2), p.1689-1699
Hauptverfasser: Zhang, Wenli, Li, Caibin, Li, Guitong, Lin, Qimei, Zhao, Xiaorong, He, Yi, Liu, Yanxiang, Luo, Zhenbao
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container_issue 2
container_start_page 1689
container_title Journal of soil science and plant nutrition
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creator Zhang, Wenli
Li, Caibin
Li, Guitong
Lin, Qimei
Zhao, Xiaorong
He, Yi
Liu, Yanxiang
Luo, Zhenbao
description It is important to consider tobacco stalks as sources of biochar and improve the soil quality of tobacco-producing areas in Southwest China. Therefore, in this study, we investigated the effects of biochar produced from tobacco stalks on soil inorganic phosphorus (P) fractions in bulk and rhizosphere soils. We also analyzed the factors influencing these effects in tobacco-planting fields. Biochar was applied to two experimental fields in Heishi and Qianxi in Bijie City, Guizhou Province in China, at application rates of 0, 5, 20, and 40 t ha −1 . Subsequently, the soil inorganic P (P i ) fractions, pH, and exchangeable and hydrolytic acidities were analyzed, while the factors influencing the soil P i fractions were determined by redundancy analysis (RDA). The results indicated that the biochar application rate, experimental site, and tobacco roots all affected the soil P i fractions. Aluminum-phosphate (Al-P), iron-phosphate (Fe-P), and occluded-phosphate (O-P) levels in the bulk soil had significantly increased with biochar application in the Qianxi site. Meanwhile, there was a reduction in Al-P, Fe-P, and O-P levels in the rhizosphere soil in the Heishi site but not in the Qianxi site. The calcium-phosphate (Ca-P) levels in the soil were also greatly reduced in the Heishi site, while in the Qianxi site, the Ca-P levels were relatively constant in the bulk soil and increased in the rhizosphere soil. Furthermore, the exchangeable and hydrolytic acidities decreased with increasing biochar application. Soil P i fractions varied according to biochar application rate and experimental site. We found that 20 t ha −1 was an appropriate biochar application rate for enhancing soil P i fractions. In addition, the soil P i fractions were negatively correlated with the dissolved organic carbon (DOC) content but were positively correlated with the hydrolytic acidity.
doi_str_mv 10.1007/s42729-021-00472-6
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Therefore, in this study, we investigated the effects of biochar produced from tobacco stalks on soil inorganic phosphorus (P) fractions in bulk and rhizosphere soils. We also analyzed the factors influencing these effects in tobacco-planting fields. Biochar was applied to two experimental fields in Heishi and Qianxi in Bijie City, Guizhou Province in China, at application rates of 0, 5, 20, and 40 t ha −1 . Subsequently, the soil inorganic P (P i ) fractions, pH, and exchangeable and hydrolytic acidities were analyzed, while the factors influencing the soil P i fractions were determined by redundancy analysis (RDA). The results indicated that the biochar application rate, experimental site, and tobacco roots all affected the soil P i fractions. Aluminum-phosphate (Al-P), iron-phosphate (Fe-P), and occluded-phosphate (O-P) levels in the bulk soil had significantly increased with biochar application in the Qianxi site. Meanwhile, there was a reduction in Al-P, Fe-P, and O-P levels in the rhizosphere soil in the Heishi site but not in the Qianxi site. The calcium-phosphate (Ca-P) levels in the soil were also greatly reduced in the Heishi site, while in the Qianxi site, the Ca-P levels were relatively constant in the bulk soil and increased in the rhizosphere soil. Furthermore, the exchangeable and hydrolytic acidities decreased with increasing biochar application. Soil P i fractions varied according to biochar application rate and experimental site. We found that 20 t ha −1 was an appropriate biochar application rate for enhancing soil P i fractions. 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Therefore, in this study, we investigated the effects of biochar produced from tobacco stalks on soil inorganic phosphorus (P) fractions in bulk and rhizosphere soils. We also analyzed the factors influencing these effects in tobacco-planting fields. Biochar was applied to two experimental fields in Heishi and Qianxi in Bijie City, Guizhou Province in China, at application rates of 0, 5, 20, and 40 t ha −1 . Subsequently, the soil inorganic P (P i ) fractions, pH, and exchangeable and hydrolytic acidities were analyzed, while the factors influencing the soil P i fractions were determined by redundancy analysis (RDA). The results indicated that the biochar application rate, experimental site, and tobacco roots all affected the soil P i fractions. Aluminum-phosphate (Al-P), iron-phosphate (Fe-P), and occluded-phosphate (O-P) levels in the bulk soil had significantly increased with biochar application in the Qianxi site. 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Therefore, in this study, we investigated the effects of biochar produced from tobacco stalks on soil inorganic phosphorus (P) fractions in bulk and rhizosphere soils. We also analyzed the factors influencing these effects in tobacco-planting fields. Biochar was applied to two experimental fields in Heishi and Qianxi in Bijie City, Guizhou Province in China, at application rates of 0, 5, 20, and 40 t ha −1 . Subsequently, the soil inorganic P (P i ) fractions, pH, and exchangeable and hydrolytic acidities were analyzed, while the factors influencing the soil P i fractions were determined by redundancy analysis (RDA). The results indicated that the biochar application rate, experimental site, and tobacco roots all affected the soil P i fractions. Aluminum-phosphate (Al-P), iron-phosphate (Fe-P), and occluded-phosphate (O-P) levels in the bulk soil had significantly increased with biochar application in the Qianxi site. Meanwhile, there was a reduction in Al-P, Fe-P, and O-P levels in the rhizosphere soil in the Heishi site but not in the Qianxi site. The calcium-phosphate (Ca-P) levels in the soil were also greatly reduced in the Heishi site, while in the Qianxi site, the Ca-P levels were relatively constant in the bulk soil and increased in the rhizosphere soil. Furthermore, the exchangeable and hydrolytic acidities decreased with increasing biochar application. Soil P i fractions varied according to biochar application rate and experimental site. We found that 20 t ha −1 was an appropriate biochar application rate for enhancing soil P i fractions. In addition, the soil P i fractions were negatively correlated with the dissolved organic carbon (DOC) content but were positively correlated with the hydrolytic acidity.</abstract><cop>Cham</cop><pub>Springer International Publishing</pub><doi>10.1007/s42729-021-00472-6</doi><tpages>11</tpages><orcidid>https://orcid.org/0000-0001-7845-8167</orcidid></addata></record>
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subjects Acidity
Adsorption
Agriculture
Aluminum
Biomedical and Life Sciences
Calcium
Calcium phosphates
Charcoal
Dissolved organic carbon
Ecology
Environment
Fertilizers
Fractions
Hydroxyapatite
Iron
Life Sciences
Original Paper
Phosphorus
Plant Sciences
Potassium
Precipitation
Redundancy
Rhizosphere
Soil analysis
Soil improvement
Soil quality
Soil Science & Conservation
Soils
Temperature
Tobacco
title Biochar Alters Inorganic Phosphorus Fractions in Tobacco-growing Soil
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