Saline Sodic Soils

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Chunjie Tian - One of the best experts on this subject based on the ideXlab platform.

  • Fungal community composition in Sodic Soils subjected to long-term rice cultivation
    Archives of Agronomy and Soil Science, 2019
    Co-Authors: Jiaxu Zhang, Shasha Luo, Xiaolong Lin, Jianfeng Zhang, Jiejing Zhang, Hongbin Wang, Chunjie Tian
    Abstract:

    Rice cultivation is widely used to improve Saline-Sodic Soils in Northeast China. However, the chronological effect of rice cultivation on soil fungal communities has not been studied. Therefore, t...

  • Soil ameliorants alter physicochemical properties and fungal communities in Saline-Sodic Soils of Northeast China
    Archives of Agronomy and Soil Science, 2018
    Co-Authors: Shaojie Wang, Shasha Luo, Lei Tian, Chunling Chang, Xue Zhou, Qiang Gao, Chunjie Tian
    Abstract:

    To understand the mechanisms of soil ameliorants affecting microbial communities is important for Saline-Sodic Soils reclamation. High-throughput sequencing was used to characterize the fungal comm...

  • aggregate related changes in soil microbial communities under different ameliorant applications in Saline Sodic Soils
    Geoderma, 2018
    Co-Authors: Shasha Luo, Lei Tian, Shaojie Wang, Zhichun Wang, Shaohua Shi, Fan Yang, Chunjie Tian
    Abstract:

    Abstract Soil ameliorants can improve soil physico-chemical properties and activate microbial communities in Saline-Sodic Soils. However, there has been less focus on how aggregate fractions affect soil microbial communities under different ameliorant applications. Here, we used the phospholipid fatty acid (PLFA) analysis to explore the effects of soil ameliorants on microbial communities within mega-aggregates (diameter of >2 mm, ME), macro-aggregates (diameter of 0.25–2 mm, MA), and micro-aggregates (diameter of  ME > MI. Meanwhile, the proportional abundance of arbuscular mycorrhizal fungi (AMF) varied between different aggregate fractions as follows: ME > MA > MI. Additionally, the DG treatment significantly enhanced the soil aggregate stability by increasing the AMF abundance, AMF/saprotrophic fungi ratio, and SOC content of the MI. Furthermore, soil microbial groups were highly correlated with soil SOC (P  0.25 mm diameter (P

  • grass and maize vegetation systems restore Saline Sodic Soils in the songnen plain of northeast china
    Land Degradation & Development, 2018
    Co-Authors: Shasha Luo, Jianfeng Zhang, Lei Tian, Chunling Chang, Shaojie Wang, Xue Zhou, Lam-son Phan Tran, Chunjie Tian
    Abstract:

    Establishment of an appropriate vegetation system for reclamation of Saline-Sodic Soils requires studies for specific salt-affected region(s). The phytoremediation of Saline-Sodic Soils has not been well documented in the Songnen Plain of northeast China. Thus, in this study, we aimed to investigate the effects of grass (G) and maize (Zea mays L.; M) vegetation systems, which were established for 5 years, on soil properties of 10 typical Saline-Sodic sampling sites across the Songnen Plain, in comparison with respective nonvegetated areas that were used as controls (CK) for the evaluation of variability among the sampling sites. Physicochemical properties, such as soil moisture, bulk density, porosity, saturated hydraulic conductivity, aggregate stability, pH, electric conductivity, total salt, organic C, total N, and C/N ratio, were analyzed. G and M vegetation significantly produced a 108% and 153% improvement in soil quality, respectively. Additionally, metagenomic analysis of the soil bacterial community revealed that vegetation enhanced the ability of the bacteria to survive in Saline-Sodic Soils, relative to the control. The composition of the bacterial community was highly correlated with all of the soil physicochemical properties. G vegetation had better effects than M vegetation in enhancing soil organic C, total N and aggregate stability, whereas M vegetation more favorably adjusted soil pH, physical structure, and bacterial community than G vegetation did. Collectively, these findings demonstrate that M vegetation has a greater impact than G vegetation on repairing Saline-Sodic Soils in the Songnen Plain of northeast China.

  • Grass and maize vegetation systems restore SalineSodic Soils in the Songnen Plain of northeast China
    Land Degradation & Development, 2018
    Co-Authors: Shasha Luo, Jianfeng Zhang, Lei Tian, Chunling Chang, Shaojie Wang, Xue Zhou, Lam-son Phan Tran, Chunjie Tian
    Abstract:

    Establishment of an appropriate vegetation system for reclamation of Saline-Sodic Soils requires studies for specific salt-affected region(s). The phytoremediation of Saline-Sodic Soils has not been well documented in the Songnen Plain of northeast China. Thus, in this study, we aimed to investigate the effects of grass (G) and maize (Zea mays L.; M) vegetation systems, which were established for 5 years, on soil properties of 10 typical Saline-Sodic sampling sites across the Songnen Plain, in comparison with respective nonvegetated areas that were used as controls (CK) for the evaluation of variability among the sampling sites. Physicochemical properties, such as soil moisture, bulk density, porosity, saturated hydraulic conductivity, aggregate stability, pH, electric conductivity, total salt, organic C, total N, and C/N ratio, were analyzed. G and M vegetation significantly produced a 108% and 153% improvement in soil quality, respectively. Additionally, metagenomic analysis of the soil bacterial community revealed that vegetation enhanced the ability of the bacteria to survive in Saline-Sodic Soils, relative to the control. The composition of the bacterial community was highly correlated with all of the soil physicochemical properties. G vegetation had better effects than M vegetation in enhancing soil organic C, total N and aggregate stability, whereas M vegetation more favorably adjusted soil pH, physical structure, and bacterial community than G vegetation did. Collectively, these findings demonstrate that M vegetation has a greater impact than G vegetation on repairing Saline-Sodic Soils in the Songnen Plain of northeast China.

Shasha Luo - One of the best experts on this subject based on the ideXlab platform.

  • Fungal community composition in Sodic Soils subjected to long-term rice cultivation
    Archives of Agronomy and Soil Science, 2019
    Co-Authors: Jiaxu Zhang, Shasha Luo, Xiaolong Lin, Jianfeng Zhang, Jiejing Zhang, Hongbin Wang, Chunjie Tian
    Abstract:

    Rice cultivation is widely used to improve Saline-Sodic Soils in Northeast China. However, the chronological effect of rice cultivation on soil fungal communities has not been studied. Therefore, t...

  • Soil ameliorants alter physicochemical properties and fungal communities in Saline-Sodic Soils of Northeast China
    Archives of Agronomy and Soil Science, 2018
    Co-Authors: Shaojie Wang, Shasha Luo, Lei Tian, Chunling Chang, Xue Zhou, Qiang Gao, Chunjie Tian
    Abstract:

    To understand the mechanisms of soil ameliorants affecting microbial communities is important for Saline-Sodic Soils reclamation. High-throughput sequencing was used to characterize the fungal comm...

  • aggregate related changes in soil microbial communities under different ameliorant applications in Saline Sodic Soils
    Geoderma, 2018
    Co-Authors: Shasha Luo, Lei Tian, Shaojie Wang, Zhichun Wang, Shaohua Shi, Fan Yang, Chunjie Tian
    Abstract:

    Abstract Soil ameliorants can improve soil physico-chemical properties and activate microbial communities in Saline-Sodic Soils. However, there has been less focus on how aggregate fractions affect soil microbial communities under different ameliorant applications. Here, we used the phospholipid fatty acid (PLFA) analysis to explore the effects of soil ameliorants on microbial communities within mega-aggregates (diameter of >2 mm, ME), macro-aggregates (diameter of 0.25–2 mm, MA), and micro-aggregates (diameter of  ME > MI. Meanwhile, the proportional abundance of arbuscular mycorrhizal fungi (AMF) varied between different aggregate fractions as follows: ME > MA > MI. Additionally, the DG treatment significantly enhanced the soil aggregate stability by increasing the AMF abundance, AMF/saprotrophic fungi ratio, and SOC content of the MI. Furthermore, soil microbial groups were highly correlated with soil SOC (P  0.25 mm diameter (P

  • grass and maize vegetation systems restore Saline Sodic Soils in the songnen plain of northeast china
    Land Degradation & Development, 2018
    Co-Authors: Shasha Luo, Jianfeng Zhang, Lei Tian, Chunling Chang, Shaojie Wang, Xue Zhou, Lam-son Phan Tran, Chunjie Tian
    Abstract:

    Establishment of an appropriate vegetation system for reclamation of Saline-Sodic Soils requires studies for specific salt-affected region(s). The phytoremediation of Saline-Sodic Soils has not been well documented in the Songnen Plain of northeast China. Thus, in this study, we aimed to investigate the effects of grass (G) and maize (Zea mays L.; M) vegetation systems, which were established for 5 years, on soil properties of 10 typical Saline-Sodic sampling sites across the Songnen Plain, in comparison with respective nonvegetated areas that were used as controls (CK) for the evaluation of variability among the sampling sites. Physicochemical properties, such as soil moisture, bulk density, porosity, saturated hydraulic conductivity, aggregate stability, pH, electric conductivity, total salt, organic C, total N, and C/N ratio, were analyzed. G and M vegetation significantly produced a 108% and 153% improvement in soil quality, respectively. Additionally, metagenomic analysis of the soil bacterial community revealed that vegetation enhanced the ability of the bacteria to survive in Saline-Sodic Soils, relative to the control. The composition of the bacterial community was highly correlated with all of the soil physicochemical properties. G vegetation had better effects than M vegetation in enhancing soil organic C, total N and aggregate stability, whereas M vegetation more favorably adjusted soil pH, physical structure, and bacterial community than G vegetation did. Collectively, these findings demonstrate that M vegetation has a greater impact than G vegetation on repairing Saline-Sodic Soils in the Songnen Plain of northeast China.

  • Grass and maize vegetation systems restore SalineSodic Soils in the Songnen Plain of northeast China
    Land Degradation & Development, 2018
    Co-Authors: Shasha Luo, Jianfeng Zhang, Lei Tian, Chunling Chang, Shaojie Wang, Xue Zhou, Lam-son Phan Tran, Chunjie Tian
    Abstract:

    Establishment of an appropriate vegetation system for reclamation of Saline-Sodic Soils requires studies for specific salt-affected region(s). The phytoremediation of Saline-Sodic Soils has not been well documented in the Songnen Plain of northeast China. Thus, in this study, we aimed to investigate the effects of grass (G) and maize (Zea mays L.; M) vegetation systems, which were established for 5 years, on soil properties of 10 typical Saline-Sodic sampling sites across the Songnen Plain, in comparison with respective nonvegetated areas that were used as controls (CK) for the evaluation of variability among the sampling sites. Physicochemical properties, such as soil moisture, bulk density, porosity, saturated hydraulic conductivity, aggregate stability, pH, electric conductivity, total salt, organic C, total N, and C/N ratio, were analyzed. G and M vegetation significantly produced a 108% and 153% improvement in soil quality, respectively. Additionally, metagenomic analysis of the soil bacterial community revealed that vegetation enhanced the ability of the bacteria to survive in Saline-Sodic Soils, relative to the control. The composition of the bacterial community was highly correlated with all of the soil physicochemical properties. G vegetation had better effects than M vegetation in enhancing soil organic C, total N and aggregate stability, whereas M vegetation more favorably adjusted soil pH, physical structure, and bacterial community than G vegetation did. Collectively, these findings demonstrate that M vegetation has a greater impact than G vegetation on repairing Saline-Sodic Soils in the Songnen Plain of northeast China.

Petra Marschner - One of the best experts on this subject based on the ideXlab platform.

  • drying and wetting in Saline and Saline Sodic Soils effects on microbial activity biomass and dissolved organic carbon
    Plant and Soil, 2012
    Co-Authors: Manpreet S. Mavi, Petra Marschner
    Abstract:

    Aims There are few studies on the interactive effect of salinity and Sodicity in Soils exposed to drying and wetting cycles. We conducted a study to assess the impact of multiple drying and wetting on microbial respiration, dissolved organic carbon and microbial biomass in Saline and Saline-Sodic Soils.

  • short term carbon mineralization in Saline Sodic Soils
    Biology and Fertility of Soils, 2012
    Co-Authors: Raj Setia, Deepika Setia, Petra Marschner
    Abstract:

    Previous studies have shown that carbon (C) mineralization in Saline or Sodic Soils is affected by various factors including organic C content, salt concentration and water content in Saline Soils and soil structure in Sodic Soils, but there is little information about which soil properties control carbon dioxide (CO2) emission from Saline-Sodic Soils. In this study, eight field-collected SalineSodic Soils, varying in electrical conductivity (ECe, a measure of salinity, ranging from 3 to 262 dS m−1) and sodium adsorption ratio (SARe, a measure of Sodicity, ranging from 11 to 62), were left unamended or amended with mature wheat or vetch residues (2% w/w). Carbon dioxide release was measured over 42 days at constant temperature and soil water content. Cumulative respiration expressed per gram SOC increased in the following order: unamended soilSoils and that salinity is the main influential factor for C mineralization in SalineSodic Soils.

  • Drying and wetting in Saline and Saline-Sodic Soils—effects on microbial activity, biomass and dissolved organic carbon
    Plant and Soil, 2011
    Co-Authors: Manpreet S. Mavi, Petra Marschner
    Abstract:

    Aims There are few studies on the interactive effect of salinity and Sodicity in Soils exposed to drying and wetting cycles. We conducted a study to assess the impact of multiple drying and wetting on microbial respiration, dissolved organic carbon and microbial biomass in Saline and Saline-Sodic Soils.

  • Short-term carbon mineralization in SalineSodic Soils
    Biology and Fertility of Soils, 2011
    Co-Authors: Raj Setia, Deepika Setia, Petra Marschner
    Abstract:

    Previous studies have shown that carbon (C) mineralization in Saline or Sodic Soils is affected by various factors including organic C content, salt concentration and water content in Saline Soils and soil structure in Sodic Soils, but there is little information about which soil properties control carbon dioxide (CO2) emission from Saline-Sodic Soils. In this study, eight field-collected SalineSodic Soils, varying in electrical conductivity (ECe, a measure of salinity, ranging from 3 to 262 dS m−1) and sodium adsorption ratio (SARe, a measure of Sodicity, ranging from 11 to 62), were left unamended or amended with mature wheat or vetch residues (2% w/w). Carbon dioxide release was measured over 42 days at constant temperature and soil water content. Cumulative respiration expressed per gram SOC increased in the following order: unamended soil

Lei Tian - One of the best experts on this subject based on the ideXlab platform.

  • Soil ameliorants alter physicochemical properties and fungal communities in Saline-Sodic Soils of Northeast China
    Archives of Agronomy and Soil Science, 2018
    Co-Authors: Shaojie Wang, Shasha Luo, Lei Tian, Chunling Chang, Xue Zhou, Qiang Gao, Chunjie Tian
    Abstract:

    To understand the mechanisms of soil ameliorants affecting microbial communities is important for Saline-Sodic Soils reclamation. High-throughput sequencing was used to characterize the fungal comm...

  • aggregate related changes in soil microbial communities under different ameliorant applications in Saline Sodic Soils
    Geoderma, 2018
    Co-Authors: Shasha Luo, Lei Tian, Shaojie Wang, Zhichun Wang, Shaohua Shi, Fan Yang, Chunjie Tian
    Abstract:

    Abstract Soil ameliorants can improve soil physico-chemical properties and activate microbial communities in Saline-Sodic Soils. However, there has been less focus on how aggregate fractions affect soil microbial communities under different ameliorant applications. Here, we used the phospholipid fatty acid (PLFA) analysis to explore the effects of soil ameliorants on microbial communities within mega-aggregates (diameter of >2 mm, ME), macro-aggregates (diameter of 0.25–2 mm, MA), and micro-aggregates (diameter of  ME > MI. Meanwhile, the proportional abundance of arbuscular mycorrhizal fungi (AMF) varied between different aggregate fractions as follows: ME > MA > MI. Additionally, the DG treatment significantly enhanced the soil aggregate stability by increasing the AMF abundance, AMF/saprotrophic fungi ratio, and SOC content of the MI. Furthermore, soil microbial groups were highly correlated with soil SOC (P  0.25 mm diameter (P

  • grass and maize vegetation systems restore Saline Sodic Soils in the songnen plain of northeast china
    Land Degradation & Development, 2018
    Co-Authors: Shasha Luo, Jianfeng Zhang, Lei Tian, Chunling Chang, Shaojie Wang, Xue Zhou, Lam-son Phan Tran, Chunjie Tian
    Abstract:

    Establishment of an appropriate vegetation system for reclamation of Saline-Sodic Soils requires studies for specific salt-affected region(s). The phytoremediation of Saline-Sodic Soils has not been well documented in the Songnen Plain of northeast China. Thus, in this study, we aimed to investigate the effects of grass (G) and maize (Zea mays L.; M) vegetation systems, which were established for 5 years, on soil properties of 10 typical Saline-Sodic sampling sites across the Songnen Plain, in comparison with respective nonvegetated areas that were used as controls (CK) for the evaluation of variability among the sampling sites. Physicochemical properties, such as soil moisture, bulk density, porosity, saturated hydraulic conductivity, aggregate stability, pH, electric conductivity, total salt, organic C, total N, and C/N ratio, were analyzed. G and M vegetation significantly produced a 108% and 153% improvement in soil quality, respectively. Additionally, metagenomic analysis of the soil bacterial community revealed that vegetation enhanced the ability of the bacteria to survive in Saline-Sodic Soils, relative to the control. The composition of the bacterial community was highly correlated with all of the soil physicochemical properties. G vegetation had better effects than M vegetation in enhancing soil organic C, total N and aggregate stability, whereas M vegetation more favorably adjusted soil pH, physical structure, and bacterial community than G vegetation did. Collectively, these findings demonstrate that M vegetation has a greater impact than G vegetation on repairing Saline-Sodic Soils in the Songnen Plain of northeast China.

  • Grass and maize vegetation systems restore SalineSodic Soils in the Songnen Plain of northeast China
    Land Degradation & Development, 2018
    Co-Authors: Shasha Luo, Jianfeng Zhang, Lei Tian, Chunling Chang, Shaojie Wang, Xue Zhou, Lam-son Phan Tran, Chunjie Tian
    Abstract:

    Establishment of an appropriate vegetation system for reclamation of Saline-Sodic Soils requires studies for specific salt-affected region(s). The phytoremediation of Saline-Sodic Soils has not been well documented in the Songnen Plain of northeast China. Thus, in this study, we aimed to investigate the effects of grass (G) and maize (Zea mays L.; M) vegetation systems, which were established for 5 years, on soil properties of 10 typical Saline-Sodic sampling sites across the Songnen Plain, in comparison with respective nonvegetated areas that were used as controls (CK) for the evaluation of variability among the sampling sites. Physicochemical properties, such as soil moisture, bulk density, porosity, saturated hydraulic conductivity, aggregate stability, pH, electric conductivity, total salt, organic C, total N, and C/N ratio, were analyzed. G and M vegetation significantly produced a 108% and 153% improvement in soil quality, respectively. Additionally, metagenomic analysis of the soil bacterial community revealed that vegetation enhanced the ability of the bacteria to survive in Saline-Sodic Soils, relative to the control. The composition of the bacterial community was highly correlated with all of the soil physicochemical properties. G vegetation had better effects than M vegetation in enhancing soil organic C, total N and aggregate stability, whereas M vegetation more favorably adjusted soil pH, physical structure, and bacterial community than G vegetation did. Collectively, these findings demonstrate that M vegetation has a greater impact than G vegetation on repairing Saline-Sodic Soils in the Songnen Plain of northeast China.

Shaojie Wang - One of the best experts on this subject based on the ideXlab platform.

  • Soil ameliorants alter physicochemical properties and fungal communities in Saline-Sodic Soils of Northeast China
    Archives of Agronomy and Soil Science, 2018
    Co-Authors: Shaojie Wang, Shasha Luo, Lei Tian, Chunling Chang, Xue Zhou, Qiang Gao, Chunjie Tian
    Abstract:

    To understand the mechanisms of soil ameliorants affecting microbial communities is important for Saline-Sodic Soils reclamation. High-throughput sequencing was used to characterize the fungal comm...

  • aggregate related changes in soil microbial communities under different ameliorant applications in Saline Sodic Soils
    Geoderma, 2018
    Co-Authors: Shasha Luo, Lei Tian, Shaojie Wang, Zhichun Wang, Shaohua Shi, Fan Yang, Chunjie Tian
    Abstract:

    Abstract Soil ameliorants can improve soil physico-chemical properties and activate microbial communities in Saline-Sodic Soils. However, there has been less focus on how aggregate fractions affect soil microbial communities under different ameliorant applications. Here, we used the phospholipid fatty acid (PLFA) analysis to explore the effects of soil ameliorants on microbial communities within mega-aggregates (diameter of >2 mm, ME), macro-aggregates (diameter of 0.25–2 mm, MA), and micro-aggregates (diameter of  ME > MI. Meanwhile, the proportional abundance of arbuscular mycorrhizal fungi (AMF) varied between different aggregate fractions as follows: ME > MA > MI. Additionally, the DG treatment significantly enhanced the soil aggregate stability by increasing the AMF abundance, AMF/saprotrophic fungi ratio, and SOC content of the MI. Furthermore, soil microbial groups were highly correlated with soil SOC (P  0.25 mm diameter (P

  • grass and maize vegetation systems restore Saline Sodic Soils in the songnen plain of northeast china
    Land Degradation & Development, 2018
    Co-Authors: Shasha Luo, Jianfeng Zhang, Lei Tian, Chunling Chang, Shaojie Wang, Xue Zhou, Lam-son Phan Tran, Chunjie Tian
    Abstract:

    Establishment of an appropriate vegetation system for reclamation of Saline-Sodic Soils requires studies for specific salt-affected region(s). The phytoremediation of Saline-Sodic Soils has not been well documented in the Songnen Plain of northeast China. Thus, in this study, we aimed to investigate the effects of grass (G) and maize (Zea mays L.; M) vegetation systems, which were established for 5 years, on soil properties of 10 typical Saline-Sodic sampling sites across the Songnen Plain, in comparison with respective nonvegetated areas that were used as controls (CK) for the evaluation of variability among the sampling sites. Physicochemical properties, such as soil moisture, bulk density, porosity, saturated hydraulic conductivity, aggregate stability, pH, electric conductivity, total salt, organic C, total N, and C/N ratio, were analyzed. G and M vegetation significantly produced a 108% and 153% improvement in soil quality, respectively. Additionally, metagenomic analysis of the soil bacterial community revealed that vegetation enhanced the ability of the bacteria to survive in Saline-Sodic Soils, relative to the control. The composition of the bacterial community was highly correlated with all of the soil physicochemical properties. G vegetation had better effects than M vegetation in enhancing soil organic C, total N and aggregate stability, whereas M vegetation more favorably adjusted soil pH, physical structure, and bacterial community than G vegetation did. Collectively, these findings demonstrate that M vegetation has a greater impact than G vegetation on repairing Saline-Sodic Soils in the Songnen Plain of northeast China.

  • Grass and maize vegetation systems restore SalineSodic Soils in the Songnen Plain of northeast China
    Land Degradation & Development, 2018
    Co-Authors: Shasha Luo, Jianfeng Zhang, Lei Tian, Chunling Chang, Shaojie Wang, Xue Zhou, Lam-son Phan Tran, Chunjie Tian
    Abstract:

    Establishment of an appropriate vegetation system for reclamation of Saline-Sodic Soils requires studies for specific salt-affected region(s). The phytoremediation of Saline-Sodic Soils has not been well documented in the Songnen Plain of northeast China. Thus, in this study, we aimed to investigate the effects of grass (G) and maize (Zea mays L.; M) vegetation systems, which were established for 5 years, on soil properties of 10 typical Saline-Sodic sampling sites across the Songnen Plain, in comparison with respective nonvegetated areas that were used as controls (CK) for the evaluation of variability among the sampling sites. Physicochemical properties, such as soil moisture, bulk density, porosity, saturated hydraulic conductivity, aggregate stability, pH, electric conductivity, total salt, organic C, total N, and C/N ratio, were analyzed. G and M vegetation significantly produced a 108% and 153% improvement in soil quality, respectively. Additionally, metagenomic analysis of the soil bacterial community revealed that vegetation enhanced the ability of the bacteria to survive in Saline-Sodic Soils, relative to the control. The composition of the bacterial community was highly correlated with all of the soil physicochemical properties. G vegetation had better effects than M vegetation in enhancing soil organic C, total N and aggregate stability, whereas M vegetation more favorably adjusted soil pH, physical structure, and bacterial community than G vegetation did. Collectively, these findings demonstrate that M vegetation has a greater impact than G vegetation on repairing Saline-Sodic Soils in the Songnen Plain of northeast China.