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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2023, Vol. 17 Issue (4) : 42    https://doi.org/10.1007/s11783-023-1642-z
RESEARCH ARTICLE
The distribution and availability of phosphorus fractions in restored cut slopes soil aggregates: a case study of subalpine road, Southwest China
Mengke Zhu1, Bocong Huang1, Shenghao Ai2,3, Zongyang Liu1, Xiaoyan Ai1, Meihua Sheng1, Yingwei Ai1()
1. Key Laboratory of Bio-Resource and Eco-Environment of Ministry of Education, College of Life Sciences, State Key Laboratory of Hydraulics and Mountain River Engineering, Sichuan University, Chengdu 610065, China
2. Chengdu Institute of Organic Chemistry, Chinese Academy of Sciences, Chengdu 610041, China
3. University of Chinese Academy of Sciences, Beijing 100049, China
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Abstract

● There was no significant difference in soil aggregates TP along altitude gradient.

● Overall, PAC dropped steadily as aggregate size increased.

● In soil aggregate sizes, TPi > TPo > R-P at 3009,3347 and 3654 m except 3980 m.

● Active NaHCO3-Pi was the main AP source.

● Proportion of small aggregate sizes was emphasized to increase AP storage.

The distribution and availability of phosphorus (P) fractions in restored cut slope soil aggregates, along altitude gradients, were analyzed. Samples were collected at 3009, 3347, 3654 and 3980 m of altitude. We examined soil aggregates total phosphorus (TP), available phosphorus (AP) and phosphorus activation coefficient (PAC), and discovered that there was no significant difference in TP levels between all four altitudes samples (p > 0.05). However, there was a significant difference in AP at 3009, 3347 and 3980 m of altitude (p < 0.05). At the altitudes of 3009, 3347 and 3654 m, the AP accumulation in small size aggregates was more advantageous. Overall, PAC dropped steadily as soil aggregates sizes increased, as shown: PAC (3654 m) > PAC (3347 m) > PAC (3009 m) > PAC (3980 m). In all particle size soil aggregates, the distribution of the P fractions was as follows: total inorganic phosphorus (TPi) > total organic phosphorus (TPo) > residual phosphorus (R-P), at 3009, 3347 and 3654 m, but a different registry was observed at 3980 m of altitude: TPo > TPi > R-P. Through correlation and multiple stepwise regression analysis, it was concluded that active NaHCO3-Pi was the main AP source. It was also suggested that more attention should be given to the ratio of small particle size aggregates to increase soil AP storage. In order to improve the activation capacity and supply of soil P, along with promotion of the healthy development of soil ecosystem on slope land, it was suggest that inorganic P fertilizer and P activator could be added to soil at both low (3009 m) and high altitudes (3980 m).

Keywords Altitude gradient      Restored cut slopes      Soil aggregates      Phosphorus fraction      Available phosphorus     
Corresponding Author(s): Yingwei Ai   
Issue Date: 24 October 2022
 Cite this article:   
Mengke Zhu,Bocong Huang,Shenghao Ai, et al. The distribution and availability of phosphorus fractions in restored cut slopes soil aggregates: a case study of subalpine road, Southwest China[J]. Front. Environ. Sci. Eng., 2023, 17(4): 42.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-023-1642-z
https://academic.hep.com.cn/fese/EN/Y2023/V17/I4/42
Fig.1  Study area location and sampling points distribution (four altitude gradients).
Fig.2  Schematic diagram of P fractions extraction sequence in soil aggregates.
Altitude gradient (m) Soil aggregate sizes (mm)
< 0.25 0.25–0.5 0.5–1 1–2 2–5 > 5
3009 639.75±66.45Aa 649.61±50.67Aa 661.40±44.05Aa 652.23±59.29Aa 629.82±39.16Aa 664.64±63.50Aa
3347 494.55±41.39Aa 579.86±48.26Aa 555.7±35.73ABa 557.81±3.96ABa 546.52±33.41Aa 548.74±16.33ABa
3654 509.26±67.32Aa 496.00±79.47Aa 410.43±83.43Ba 406.5±63.55Ba 382.8±61.41Ba 425.41±39.65Ba
3980 641.71±77.04Aa 643.87±59.48Aa 743.39±101.14Aa 716.91±73.65Aa 621.90±7.21Aa 661.26±73.84Aa
Tab.1  TP content (mg/kg) in soil aggregates along altitude gradient
Fig.3  Variation trends of TP and AP in soil aggregate sizes along altitude gradient.
Altitude gradient (m) Soil aggregate sizes (mm)
< 0.25 0.25–0.5 0.5–1 1–2 2–5 > 5
3009 12.65±0.85Ca 11.67±0.82Bab 10.99±0.74BCab 10.23±1.26Bab 8.78±0.93Bbc 7.25±0.85Bc
3347 20.24±1.50Ba 19.29±0.80Aa 15.08±0.13ABb 13.68±1.03ABb 12.08±0.92Bb 12.33±0.89Bb
3654 29.67±4.26Aa 24.24±3.40Aa 19.74±3.18Aa 20.59±4.10Aa 21.18±4.25Aa 21.52±5.43Aa
3980 7.36±0.50Cb 9.23±0.19Ba 9.39±0.07Ca 9.54±0.12Ba 8.99±0.51Ba 9.06±0.28Ba
Tab.2  AP (mg/kg) content in soil aggregates along altitude gradient
Fig.4  Variation trends of soil aggregates PAC along altitude gradient. Notes: Mean±SE. PAC= phosphorus activation coefficient.
Indicators AP TP H2O-Pi NaHCO3-Pi NaHCO3-Po NaOH-Pi NaOH-Po DHCl-Pi HHCl-Pi HHCl-Po
TP –0.794**
H2O-Pi –0.052 0.190
NaHCO3-Pi 0.851** –0.671** 0.120
NaHCO3-Po –0.089 0.377 –0.034 0.219
NaOH-Pi 0.240 –0.117 –0.361 0.522** 0.768**
NaOH-Po –0.287 0.535** –0.152 –0.020 0.819** 0.687**
DHCl-Pi –0.220 0.239 0.229 –0.531** –0.669** –0.934** –0.581**
HHCl-Pi –0.796** 0.793** 0.208 –0.845** –0.110 –0.564** 0.033 0.623**
HHCl-Po –0.878** 0.903** 0.033 –0.701** 0.433* 0.047 0.621** 0.006 0.685**
R-P –0.383 0.468* –0.034 –0.082 0.641** 0.569** 0.652** –0.583** 0.014 0.511*
Tab.3  Correlation analysis of P related indicators and fractions
Fig.5  The P form fractions content in soil aggregate sizes along altitude gradient.
Fig.6  The P stability fractions content in soil aggregate sizes along altitude gradient.
Abstract of model Abstract of regression equation
Items Constant NaHCO3-Pi (X2) HHCl-Po (X8)
R2 0.881 Coefficient of equation 18.033 0.233 −0.077
F value 77.851 Sig. 0.000 0.000 0.000
Durbin-Watson value 1.836 Collinear VIF values 1.964 1.964
Sig. 0.000
Maximum standard residual 2.167 Regression equation Y = 18.033+0.233X2−0.077X8
Tab.4  Multiple stepwise regression analysis of soil aggregates P fractions (X) on AP (Y)
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