生物炭添加对盐碱土浑水入渗土壤水盐运移特性的影响

    Influences of biochar addition on soil water and salt transport of infiltration with muddy water in saline-alkali soil

    • 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,该研究采用室内一维土柱入渗,研究了在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,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;而生物炭添加明显减少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,生物炭通过调控离子吸附与孔隙结构优化水盐平衡的机制,可为盐碱地浑水灌溉与生物炭协同改良提供理论依据。

       

      Abstract: Muddy water irrigation has been limited to a wide application during agricultural production in recent years. Current challenges also remain on the water shortage and soil salinization in the arid and semi-arid regions. In this study, a series of experiments was conducted on a one-dimensional soil column infiltration in the laboratory. A systematic investigation was also made to explore the effects of different salt contents (S0: 0.80 g/kg, S1: 4.81 g/kg, and S2: 9.45 g/kg) and biochar addition amounts (B0: 0, B1: 0.5%, B2: 1%, and B3: 2%) on the soil water transport, salt ion distribution and leaching under clear water (ρ0: 0) and muddy water (ρ1: 4%) infiltration. The results showed that the cumulative infiltration amount significantly decreased with the increase of salt content (S) and biochar (B). Compared with the clear water (ρ0), the turbid water (ρ1) was reduced by 18.05% to 31.57%. The medium (S1) and high salt (S2) treatments were 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) was reduced by 0.75% to 21.16%, compared with no addition (B0). The Kostiakov model (coefficient of determination (R2)>0.88, root mean square error <0.09 cm/min) was more suitable to simulate 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) were followed by the power function. The turbid water prolonged the time to reach the bottom of the soil column increased by 10.50% to 27.93%. The 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 showed that the moisture content decreased with depth, while the electrical conductivity increased. The turbid water was reduced the average moisture content by 0.52% to 4.37%, whereas, the electrical conductivity increased by 1.78% to 16.74%; The moisture content was reduced by 9.09% to 11.59% in the high salt (S2), leading to a sharp increase in the electrical conductivity by 215.21% to 314.95%; While the biochar (B3) increased the moisture content by 2.61% to 5.53%, whereas, the electrical conductivity was reduced by 10.23% to 23.80%. Except for the 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 the salt content. There was a more significant increase in the muddy water than that in the clear water treatment; While the biochar addition significantly reduced the contents of Na+ and Cl, thus promoting the retention of K+ and Ca2+. The high salt content (S2) exacerbated the salt accumulation to reduce 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. The sediment concentration and salt content of turbid water inhibited the water transport due to the pore blockage and osmotic pressure. The biochar optimized the water salt balance to regulate the ion adsorption and pore structure. The finding can also provide a theoretical basis for the synergistic improvement of the turbid water irrigation and biochar in saline alkali land.

       

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