Impacts of simulated acid rain on soil organic matter and metal aluminum and iron ions leaching from red soil in central south China

Author(s):  
Wenjie Tian ◽  
Fangni Zhao ◽  
Xuwen He ◽  
Fasheng Li
Soil Research ◽  
2009 ◽  
Vol 47 (3) ◽  
pp. 286 ◽  
Author(s):  
Yanyu Bao ◽  
Qixing Zhou ◽  
Yingying Wang

The adsorption characteristics of tetracycline by 2 soils including a clay-rich soil (cinnamon soil) and an iron oxide-rich soil (red soil) were investigated as a function of soil organic matter (SOM). SOM is the main adsorbent for tetracycline in the soil environment. The results indicated that the adsorption kinetics of tetracycline by the different soils with or without organic matter was described by the Elovich equation and the exponent equation. The adsorption of tetracycline on red soil was quite rapid and equilibrium could be reached after 5 h. In contrast, the concentration of tetracycline in cinnamon soil reached equilibrium after 11 h. The difference in equilibrium time in cinnamon soil and red soil was caused by their dominant components for adsorption, including clays, organic matter, and Al/Fe hydrous oxides. It took longer for the penetration of tetracycline into the interlayers between clays and organic matter in cinnamon soil, but tetracycline needed less time for adsorption through surface complexation on oxide surfaces of red soil. Removing SOM from soil markedly shortened the equilibrium time (7 h) of adsorption and reduced the equilibrium concentration (Cs) in cinnamon soil, but not in red soil, because of different dominant components for adsorption in the 2 natural soils. In natural and SOM-free soils, >98% of tetracycline in solution could be sorbed. The adsorption of tetracycline on natural and SOM-free soils was well described by Freundlich adsorption isotherms. Batch adsorption experiments showed that the adsorption of tetracycline on natural red soil was stronger than that on natural cinnamon soil. Adsorption capacity (KF) decreased with an increase in SOM removed from soil, which is attributed to the effect of tetracycline sorbed by SOM in different soils. However, SOM affected the adsorption intensity (n) of different soils diversely; there was a decrease for red soil and an increase for cinnamon soil. In particular, red soil with high Al/Fe hydrous oxides had higher adsorption affinities than cinnamon soil.


CATENA ◽  
2018 ◽  
Vol 162 ◽  
pp. 270-277 ◽  
Author(s):  
Fan Yang ◽  
Jing Tian ◽  
Jeroen Meersmans ◽  
Huajun Fang ◽  
Hao Yang ◽  
...  

2007 ◽  
Vol 190 (1-4) ◽  
pp. 171-181 ◽  
Author(s):  
C. Y. Du ◽  
G. M. Zeng ◽  
G. Zhang ◽  
L. Tang ◽  
X. D. Li ◽  
...  

2012 ◽  
Vol 123 ◽  
pp. 78-86 ◽  
Author(s):  
Dan Li ◽  
Xiuzhi Chen ◽  
Zhiping Peng ◽  
Shuisen Chen ◽  
Weiqi Chen ◽  
...  

2019 ◽  
Vol 12 (1) ◽  
pp. 280 ◽  
Author(s):  
Hui Wei ◽  
Yalan Liu ◽  
Huimin Xiang ◽  
Jiaen Zhang ◽  
Saifei Li ◽  
...  

Soil has the nature of acidity and alkalinity, mostly indicated by soil pH that could greatly affect soil ecological processes and functions. With exogenous inputs of acidic materials (such as acid rain), soils may more or less resist to maintain their pH levels within specific thresholds by various buffering processes. It has been well established that soil properties such as cation exchange capacity (CEC), soil organic matter (SOM), and clay content play important roles in mitigating the effects of acid inputs, but the factors varied across soils. This microcosm experiment was conducted to investigate changes in the soil pH and quantitatively estimate the critical pH threshold of simulated acid rain for three highly weathered soils (red soil, lateritic red soil, and latosol) that are typical soil types widely distributed across the world’s subtropical and tropical climatic zones, as well as important influential factors, after continuously adding different levels of simulated acid rain on the surface of soil cores. The results showed that the change in the soil pH was not significantly different among the three soils, although it was exponentially related to soil CEC and clay content. Resultantly, the latosol that had high soil CEC and clay content was more resistant to simulated acid rain, especially when relatively weak simulated acid rain treatments were applied. The lateritic red soil that contained the lowest soil CEC and clay content showed the greatest decline in the soil pH under the strongest simulated acid rain treatment of pH being 2.5. Furthermore, we estimated the critical pH threshold of simulated acid rain for the three soils and observed that it was considerably different among the soils. Surprisingly, the pH threshold of simulated acid rain was also positively related to the soil CEC and clay content, therefore making the highest pH threshold in the latosol. Our results imply that soil CEC and clay content may play critical roles in the soil acid-buffering processes from two aspects; it could not only contribute to the soil acid-buffering capacity, but also affect the threshold of acidity of acid rain below which abrupt soil acidification may occur.


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