Author
Listed:
- Jiayue Yang
(Guangdong Provincial Key Laboratory of Eco-Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Department of Ecology, College of Natural Resources and Environment, South China Agricultural University, Guangzhou 510642, China)
- Hui Wei
(Guangdong Provincial Key Laboratory of Eco-Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Department of Ecology, College of Natural Resources and Environment, South China Agricultural University, Guangzhou 510642, China
Guangdong Engineering Technology Research Centre of Modern Eco-Agriculture and Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Key Laboratory of Agro-Environment in the Tropics, Ministry of Agriculture and Rural Affairs, South China Agricultural University, Guangzhou 510642, China)
- Jiaen Zhang
(Guangdong Provincial Key Laboratory of Eco-Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Department of Ecology, College of Natural Resources and Environment, South China Agricultural University, Guangzhou 510642, China
Guangdong Engineering Technology Research Centre of Modern Eco-Agriculture and Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Key Laboratory of Agro-Environment in the Tropics, Ministry of Agriculture and Rural Affairs, South China Agricultural University, Guangzhou 510642, China)
- Zhaoji Shi
(Guangdong Provincial Key Laboratory of Eco-Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Department of Ecology, College of Natural Resources and Environment, South China Agricultural University, Guangzhou 510642, China)
- Hongru Li
(Guangdong Provincial Key Laboratory of Eco-Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Department of Ecology, College of Natural Resources and Environment, South China Agricultural University, Guangzhou 510642, China
Guangdong Engineering Technology Research Centre of Modern Eco-Agriculture and Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Key Laboratory of Agro-Environment in the Tropics, Ministry of Agriculture and Rural Affairs, South China Agricultural University, Guangzhou 510642, China)
- Yanqiong Ye
(Guangdong Provincial Key Laboratory of Eco-Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Department of Ecology, College of Natural Resources and Environment, South China Agricultural University, Guangzhou 510642, China)
- Ahmed Ibrahim Abdo
(Guangdong Provincial Key Laboratory of Eco-Circular Agriculture, South China Agricultural University, Guangzhou 510642, China
Department of Ecology, College of Natural Resources and Environment, South China Agricultural University, Guangzhou 510642, China)
Abstract
Soil acidification is a severe environmental problem around the world. Soil pH buffering capacity (pHBC) is the intrinsic factor affecting the soil acidification rate and is intensively impacted by anthropogenic and natural conditions. However, composite assessments of the effects of land use and soil type on soil pHBC are still limited. Therefore, we collected samples of five soil types (red soil, lateritic red soil, latosol, paddy soil and acid sulphate soil) from two land use patterns of agricultural and adjacent forest fields at different depths (0–10 cm, 10–20 cm and 20–30 cm) in South China, aiming to investigate the effects of land use and soil type on soil pHBC in this region. The results show that land use, soil type and their interactions greatly influence soil pHBC and physico-chemical properties. Forest soils have a significantly higher pHBC (11.40–49.50 mmol·kg −1 soil·unit −1 pH), cation exchange capacity (CEC), exchangeable Al 3+ (EAl 3+ ) and clay content than agricultural soils. Acid sulphate soil has the highest pHBC (49.27–117.83 mmol·kg −1 soil·unit −1 pH) values and exchangeable acid (EA) content among all investigated soil types, whereas lateritic red soil has the lowest pHBC (10.56–31.71 mmol·kg −1 soil·unit −1 pH). In agricultural fields, soil pHBC is positively related to CEC, soil organic carbon (SOC) and EA, indicating that agricultural soils may be in a cation exchange buffering stage. The soil pHBC of forest fields is positively correlated with SOC and EAl 3+ , implying that forest soils may be in the Al buffering stage. In conclusion, soil pHBC would vary with different land use forms and soil types, in which a series of key complex physico-chemical processes and interactions would occur to regulate soil pH buffering capacity.
Suggested Citation
Jiayue Yang & Hui Wei & Jiaen Zhang & Zhaoji Shi & Hongru Li & Yanqiong Ye & Ahmed Ibrahim Abdo, 2022.
"Land Use and Soil Type Exert Strongly Interactive Impacts on the pH Buffering Capacity of Acidic Soils in South China,"
Sustainability, MDPI, vol. 14(19), pages 1-13, October.
Handle:
RePEc:gam:jsusta:v:14:y:2022:i:19:p:12891-:d:937427
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