4.7 Article

Soil acidification and loss of base cations in a subtropical agricultural watershed

Journal

SCIENCE OF THE TOTAL ENVIRONMENT
Volume 827, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.scitotenv.2022.154338

Keywords

Soil acidification; Base cations loss; Exchangeable base cations; Red soil; Nitrogen fertilization; Agricultural watershed

Funding

  1. National Natural Science Foundation of China [U1901601, 41877010, 41771251, 42107334]
  2. DIKU exchange program (Norway-China) [UTF-2016-10089]
  3. University of Chinese Academy of Sciences (UCAS)

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Soil acidification and base cation loss are significant problems in the subtropical red soil region of China, particularly in agroecosystems with high nitrogen fertilization. This study assessed the current status and future risk of soil acidification in a typical agricultural watershed using a two-year monitoring approach. The results showed that while significant soil acidification occurred, surface water acidification was minor, indicating the buffer capacity of the soils. However, there was a substantial loss of base cations, depleting the exchangeable pool in the watershed and posing a serious threat to soil recovery from acidification.
Soil acidification along with base cations loss degrades soil quality and is a major environmental problem, especially in agroecosystems with extensive nitrogen (N) fertilization. So far, the rates of proton (H+) production and real soil acidification (loss of base cations) remain unclear in subtropical agricultural watersheds. To assess the current status and future risk of soil acidification in subtropical red soil region of China, a two-year monitoring was conducted in a typical agricultural watershed with upland, paddy fields, and orchards where high N fertilizers are applied (320 kg N ha(-1) yr(-1)). H+ production, neutralization and base cations losses were quantified based on the inputs (rainwater, inflow of water, and fertilizer) and outputs (outflow of water, groundwater drainage, and plant uptake) of major elements (K+, Ca2+, Na+, Mg2+, Al3+, NH4+, NO3-, SO42-, Cl-, and H+). The result showed that total H+ production in the watershed was 5152 molc ha(-1) yr(-1). N transformation was the most important H+ source (68%), followed by excess plant uptake of cations (25%) and H+ deposition (7%). Base cations exchange and weathering of minerals (3842 mol(c) ha(-1) yr(-1)) dominated H+ neutralization, followed by SO42- adsorption (1081 molc ha(-1) yr(-1)), while H+ and Al3+ leaching amounted to 431 molc ha(-1) yr(-1), only. These results state clearly that despite significant soil acidification, the acidification of surface waters is minor, implying that soils have buffered substantially the net H+ addition. As a result of soil buffering, there was abundant loss of base cations, whose rate is significantly higher than the previously reported weathering rate of minerals in red soils (3842 vs 230-1080 mol(c) ha(-1) yr(-1)). This suggests that the pool of exchangeable base cations is being depleted in the watershed, increasing the vulnerability of the watershed, and posing a serious threat to future recovery of soils from acidification.

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