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生物炭添加对盐碱土浑水入渗土壤水盐运移特性的影响

Effects of organic fertilizer on soil water transport, evaporation and leaching under muddy water irrigation

  • 摘要: 针对目前浑水灌溉还较少应用于农业生产的现状,结合干旱半干旱地区水资源短缺和土壤盐碱化的问题,本研究采用室内一维土柱入渗,该研究浑水和清水入渗条件下,不同含盐量和生物炭添加量对土壤水分运移、盐分离子分布及淋溶特性的影响。结果表明:含盐量及生物炭添加量增加显著抑制累积入渗量、入渗速率和湿润锋运移(Kostiakov模型比Philip模型拟合效果更优),浑水入渗相较于清水抑制更为明显。含盐量升高导致土壤含水率降低、电导率上升,而生物炭添加可提升土壤含水率,降低电导率。除土壤钾离子(K+)外,土壤钙离子(Ca2+)、镁离子(Mg2+)、钠离子(Na+)、硫酸根离子(SO42−)、氯离子(Cl)和碳酸氢根离子(HCO3)含量随含盐量的增加均呈增加趋势,且浑水处理较清水增加更显著;而生物炭添加显著减少Na+和Cl含量,促进K+和Ca2+保留。高含盐量加剧盐分累积,且减少淋溶液体积,并表现出较高的淋溶液电导率。该研究揭示了浑水灌溉与含盐量通过孔隙堵塞和渗透压效应抑制水分运移,而生物炭通过调控离子吸附与孔隙结构优化水盐平衡,可为盐碱地浑水灌溉与生物炭协同改良提供理论依据。

     

    Abstract: In view of the current limited application of muddy water irrigation in agricultural production, and considering the problems of water shortage and soil salinization in arid and semi-arid regions, this study conducted one-dimensional soil column infiltration experiments in the laboratory to investigate the effects of different salt contents (S0: 0.80 g/kg, S1: 4.81 g/kg, S2: 9.45 g/kg) and biochar addition amounts (B0: 0, B1: 1%, B2: 2%, B3: 3%) on soil water transport, salt ion distribution and leaching characteristics under clear water (ρ0: 0) and muddy water (ρ1: 4%) infiltration conditions. The results showed that the cumulative infiltration amount significantly decreased with the increase of salt content (S) and biochar (B). Compared with clear water (ρ0), the turbid water (ρ1) reduced by 18.05% to 31.57%. The medium (S1) and high salt (S2) treatments reduced by 9.40% to 18.58% and 15.38% to 23.86% respectively compared with the low salt (S0) treatment. The addition of biochar (B1/B2/B3) reduced by 0.75% to 21.16% compared with no addition (B0). The Kostiakov model (R2>0.88, SRMSE<0.09 cm/min) was more suitable for simulating the infiltration rate than the Philip model. Its parameter K decreased with the increase of S and B, while α was the opposite. The distance of the wetting front migration (F) and time (t) conformed to the power function (F=Ctᴰ). The turbid water prolonged the time to reach the bottom of the soil column by 10.50% to 27.93%, and S and B further delayed the migration. The fitting parameters C and D were negatively exponentially correlated with S and B (R2 > 0.92). The soil profile analysis shows that the moisture content decreases with depth, while the electrical conductivity increases. The turbid water reduces the average moisture content by 0.52% to 4.37%, and increases the electrical conductivity by 1.78% to 16.74%; the high salt (S2) reduces the moisture content by 9.09% to 11.59%, and causes a sharp increase in the electrical conductivity by 215.21% to 314.95%; while the biochar (B3) increases the moisture content by 2.61% to 5.53%, and reduces the electrical conductivity by 10.23% to 23.80%. Except for soil potassium ions (K+), the contents of soil calcium ions (Ca2+), magnesium ions (Mg2+), sodium ions (Na+), sulfate ions (SO42−), chloride ions (Cl) and bicarbonate ions (HCO3) all increased with the increase in salt content, and the increase was more significant in the muddy water treatment than in the clear water treatment; while biochar addition significantly reduced the contents of Na+ and Cl, and promoted the retention of K+ and Ca2+. The high salt content (S2) exacerbates salt accumulation and reduces the volume of the leaching solution. The treatment with ρ1S2B3 showed the highest leaching solution conductivity, with an average conductivity of 88.32 mS/cm. This study reveals that the sediment concentration and salt content of turbid water inhibit water transport through pore blockage and osmotic pressure effects, while biochar optimizes water salt balance by regulating ion adsorption and pore structure, providing a theoretical basis for the synergistic improvement of turbid water irrigation and biochar in saline alkali land.

     

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