黄河东岸沙地不同配置防护林土壤水同位素特征及对土壤水分运移的指示OA
Soil Water Isotopic Characteristics and Their Implications for Soil Water Movement under Different Shelterbelt Plantation Patterns in the Eastern Yellow River Sandy Land
[目的]土壤水分运移是水循环的关键过程,探究不同配置林分土壤水分运移过程及其影响因素,可为黄土高原地区植被建设与林分结构调整提供科学依据.[方法]以宁夏黄河东岸沙地防护林柠条、刺槐、柠条×刺槐混交林为研究对象,利用氢氧稳定同位素技术和水线氘差(lc-excess)平衡方程分析柠条与刺槐在纯林和混交林中的土壤水分运移过程及其影响因素.[结果](1)各林地土壤水氢氧同位素随着土层的加深逐渐贫化并趋于稳定,柠条和刺槐混交林土壤水同位素变异系数较大且较富集,土壤入渗过程中新水与旧水混合较少.5月-10月,各林分平均土壤储水量柠条纯林(158.53 mm)<刺槐纯林(169.13 mm)<柠条×刺槐混交林(194.78 mm),土壤水分亏缺程度柠条纯林(28.7%)>刺槐纯林(24.7%)>柠条×刺槐混交林(21.1%);(2)lc-excess平衡方程结果表明,优先流相对贡献比例依次为:柠条×刺槐混交林(23.5%)>刺槐纯林(17.7%)>柠条纯林(15.9%),其中柠条纯林优先流模式出现在中深层土壤,刺槐纯林优先流模式出现在中层土壤,混交林优先流模式则出现在中层土壤;(3)影响纯林土壤水分运移的主要因素为总孔隙度,随着种植模式改变,总孔隙度对乔灌混交林土壤水分运移的影响减弱,细根生物量对乔灌混交林土壤水分运移影响增大;混交林地土壤优先流模式主要出现在降雨量较大的生长季中期,而柠条和刺槐纯林土壤优先流模式主要出现在生长季前期和后期.[结论]相较于纯林,混交种植模式能够提升土壤储水能力、减小土壤水分亏缺程度,提高土壤持水能力,此外混交种植模式增加了土壤水优先流相对贡献比例,但在降雨量较小的时期,优先流无法对根际土壤水进行补给,随着林木蒸腾耗水需求增加,林地土壤水分亏缺程度加剧,将会引起土壤干燥化.
[Objective]Soil water movement is a key process in the water cycle.Investigating the soil water movement processes and their driving factors in different forest stand configurations can provide a scientif-ic basis for vegetation construction and stand structure adjustment on the Loess Plateau.[Method]This study focused on the shelter-forest of Caragana korshinskii,Robinia pseudoacacia and the mixed forest of Caragana korshinskii × Robinia pseudoacacia in the eastern sandy land of Yellow River in Ningxia.Stable hydrogen and oxygen isotope techniques,together with the lc-excess equilibrium equation,were used to analyze soil water transport processes and the factors influencing soil water movement in pure and mixed stands.[Result](1)Soil hydrogen and oxygen isotopes in all stand types gradually became depleted and stabilized with increasing the soil depth.Compared with the pure forests,the mixed forest of Caragana kor-shinskii and Robinia pseudoacacia showed a higher coefficient of variation and relatively greater enrich-ment in soil water isotope variations,indicating less mixing between new and old water during infiltration.From May to October,the average soil water storage of each forest stand followed the order:the pure stand of Caragana korshinskii(158.53 mm)<the pure stand of Robinia pseudoacacia(169.13 mm)<mixed forest of Caragana korshinskii × Robinia pseudoacacia(Mixed)(194.78 mm).In contrast,the de-gree of soil water deficit followed the order:the pure stand of Caragana korshinskii(28.7%)>the pure stand of Robinia pseudoacacia(24.7%)>mixed forest of arbor and shrub(21.1%).(2)The lc-excess equi-librium equation showed that the relative contribution of preferential flow followed the order:mixed forest of arbor and shrub(23.5%)>the pure stand of Robinia pseudoacacia(17.7%)>the pure stand of Caragana korshinskii(15.9%).Preferential flow in the pure stand of Caragana korshinskii occurred in the mid-deep layer soil,the pure stand of Robinia pseudoacacia stands in middle layer soil,and mixed forest of arbor and shrub stands in the middle layer soil.(3)Total porosity was the primary factor influencing soil water movement in pure stands.However,its influence weakened in the mixed stand,where fine root biomass played a more important role.Preferential flow in the mixed stand mainly occurred during the middle of the growing season when rainfall was relatively high,whereas in pure stands of Caragana korshinskii and Robinia pseudoacacia,it mainly occurred during the early and late growing season.[Conclusion]Com-pared with pure forests,the mixed stands enhanced soil water storage capacity,reduced the degree of soil water deficit,and improved soil water retention.Additionally,the mixed stands enhanced the relative contri-bution proportion of preferential flow in soil water.However,during periods of low rainfall,preferential flow was insufficient to replenish the rhizosphere soil water.Astranspiration demand increased,soil water defi-cit in forest land became more severe,which may ultimately lead to soil desiccation.
王苑;韩磊;王娜娜;马云蕾;马军;马世杰;曹建华;马自良
宁夏大学地理科学与规划学院,宁夏银川 750021||中阿旱区特色资源与环境治理国际合作联合实验室,宁夏银川 750021||宁夏旱区资源评价与环境调控重点实验室,宁夏银川 750021宁夏大学地理科学与规划学院,宁夏银川 750021||中阿旱区特色资源与环境治理国际合作联合实验室,宁夏银川 750021||宁夏旱区资源评价与环境调控重点实验室,宁夏银川 750021宁夏大学地理科学与规划学院,宁夏银川 750021||中阿旱区特色资源与环境治理国际合作联合实验室,宁夏银川 750021||宁夏旱区资源评价与环境调控重点实验室,宁夏银川 750021宁夏大学地理科学与规划学院,宁夏银川 750021||中阿旱区特色资源与环境治理国际合作联合实验室,宁夏银川 750021||宁夏旱区资源评价与环境调控重点实验室,宁夏银川 750021宁夏大学林业与草业学院,宁夏银川 750021宁夏大学林业与草业学院,宁夏银川 750021宁夏大学地理科学与规划学院,宁夏银川 750021||中阿旱区特色资源与环境治理国际合作联合实验室,宁夏银川 750021||宁夏旱区资源评价与环境调控重点实验室,宁夏银川 750021海原县林业技术推广服务中心,宁夏中卫 755200
农业科技
土壤水分运移优先流氢氧稳定同位素水线氘差防护林
soil water movementpreferential flowhydrogen and oxygen stable isotopeslc-excessshelter-forest
《林业科学研究》 2026 (4)
22-33,12
国家自然科学基金项目(32460426)宁夏自然科学基金项目(2026AAC030051)
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