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High intensity rainfall in southern China has led to soil erosion on sloping farmland, causing serious ecological and environmental problems. But how the interaction of rainfall factors and growth stages influence soil erosion and nitrogen loss on sugarcane-cultivated slope under natural rainfall have not been studied considerably. This study concentrated on the in situ runoff plot observation test. Surface runoff, soil erosion, and nitrogen loss under individual natural rainfall events during the different sugarcane growth stages (seedling stage (SS), tillering stage (TS), elongation stage (ES)) from May to September in 2019 and 2020 were recorded and measured. The effects of rainfall factors (intensity and amount) on soil erosion and nitrogen loss were quantified by path analysis. The influence of rainfall factors and sugarcane planting on soil erosion and nitrogen loss was analyzed. Surface runoff, soil erosion, and nitrogen loss on sugarcane-cultivated slope were 4354.1 m/ha, 155.4 t/ha, and 25.87 kg/ha during 2019 to 2020, and were mainly concentrated in SS, accounting for 67.2%, 86.9%, and 81.9% of total surface runoff, soil erosion, and nitrogen loss, respectively. Nitrogen losses were mainly concentrated in surface runoff, accounting for 76.1% of total nitrogen loss, and the main form in surface runoff was nitrate nitrogen (NO-N, 92.9%). Under individual rainfall events, surface runoff, soil erosion, and nitrogen loss changed with the changing of rainfall characteristics and sugarcane growth. Surface runoff and nitrogen loss were obviously affected by rainfall characteristics, while the soil erosion and nitrogen loss were affected by both rainfall characteristics and sugarcane growth stages. Path analysis indicated that maximum rainfall intensities at 15 min (I) and 60 min (I) were most significant to the production of surface runoff and soil erosion with direct path coefficients of 1.19 and 1.23, respectively. NO-N and ammonium nitrogen (NH-N) losses in surface runoff were mostly influenced by maximum rainfall intensity at 30 min (I) and I with direct path coefficients of 0.89 and 3.08, respectively. NO-N and NH-N losses in sediment yield were mostly influenced by I and rainfall amount, and the direct path coefficients were 1.61 and 3.39, respectively. The main stage of soil and nitrogen loss was seedling stage, while the significant factors of rainfall characteristics affecting surface runoff, soil erosion, and nitrogen loss were quite different. The results provide theoretical support for soil erosion and quantitative rainfall erosion factors of sugarcane-cultivated slope in southern China.
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http://dx.doi.org/10.1007/s11356-023-28618-2 | DOI Listing |
Arch Environ Contam Toxicol
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PolyAnalytik, Inc., London, ON, Canada.
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Institute for Future Earth, Pusan National University, Busan 46241, Republic of Korea; Department of Biology Education, Pusan National University, Busan 46241, Republic of Korea. Electronic address:
Arsenic (As) contamination from abandoned gold mines threatens adjacent ecosystems through leaching and erosion. This study investigated how soil physicochemical properties regulate As binding forms upon initial contamination and associated ecotoxicological effects on soil invertebrates. Forest soils (0-10 cm depth) were collected from four mountainous sites across Korea with varying physicochemical properties.
View Article and Find Full Text PDFJ Environ Manage
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Agronomical Engineering Department, Technical University of Cartagena (UPCT), 30202, Cartagena, Spain. Electronic address:
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Department of Soil, Plant and Food Sciences, University of Bari Aldo Moro, Via Amendola 165/A, Bari, Italy.
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September 2025
Changsha General Survey of Natural Resources Center, China Geological Survey, Changsha 410600, China.
Soil heavy metal (HM) contamination has emerged as a critical global ecological issue. This study examines the distribution and ecological risks of ten HMs (Cu, Pb, Zn, Cr, Ni, Co, Cd, As, Hg, and Mn) in the soils of the Dabie Mountain region, a hotspot for severe soil erosion in China. Results show that slope gradient influences the spatial distribution of HMs, with steep slopes (>10°) exhibiting higher Pb and Cd concentrations compared to gentle (<5°) and moderate slopes (5-10°).
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