残茬高度对土壤风蚀量影响的试验研究

在内蒙古自治区武川县建立农田土壤风蚀试验区,采用内蒙古农业大学研制的移动式风蚀风洞和旋风分离式集沙仪,观测不同残茬高度条件下农田土壤的风蚀情况.试验结果表明:土壤风蚀量和扬起沙尘的高度随风速的增加而增加,随着作物秸秆残茬高度的增加而降低,且风蚀量与高度变化符合指数函数关系,土壤颗粒主要集中在近地表层内运动.保护性耕作可明显地提高起沙风速,减少农田土壤损失,当秸秆高度为30 cm时,风蚀量仅为传统耕地的1/4左右.     

土壤风蚀量随残茬高度的变化规律研究

在内蒙古自治区武川县建立农田土壤风蚀试验区,采用内蒙古农业大学研制的移动式风蚀风洞和旋风分离式集沙仪,直接在农田上观测不同残茬高度条件下的农田风蚀土壤损失情况。试验结果表明:土壤风蚀量和扬起沙尘的高度随风速的增加而增加,随着作物秸秆残茬高度的增加而降低,且输沙量与高度变化符合指数函数关系,土壤颗粒主要集中在近地表层内运动。保护性耕作可明显地提高启沙风速,减少农田土壤损失,当秸秆高度为30 cm时,风蚀量仅为传统耕地的1/4左右。     

农田耕作方式与土壤风蚀强度关系的风洞模拟实验

以土壤风蚀严重的河北坝上康保县为研究区,采用风洞试验的技术手段,对农田耕作方式与土壤风蚀强度的关系进行研究。结果表明,农田留茬与翻耕、农田垄向及农作物残茬高度的差异对土壤风蚀强度有较大影响。垄向平行主风向的风蚀强度大于垄向垂直主风向的风蚀强度。风速越大,垄向不同造成的风蚀强度的差异越大,尤其是当风速≥15m/s时,风蚀强度的差异表现得较为明显;风蚀强度与留茬高度呈负相关;翻耕地的风蚀强度大于任何留茬地的风蚀强度;风蚀强度与风速变化呈现出指数函数变化规律。因此,农田垄向垂直主风向、作物收获后不进行翻耕、留有适度茬高、优先种植残茬硬度较大的莜麦作物,这样的耕作方式可有效降低土壤风蚀强度,缓解河北坝上地区农田土壤风蚀状况。     

旱地保护性耕作土壤风蚀模型研究

在分析国外风蚀模型资料的基础上,建立了适用于保护性耕作的风蚀模型。该模型以小时为步长,根据气象数据、地表土壤水分、秸秆残茬覆盖率及地表粗糙度,模拟不同耕作体系下农田土壤风蚀流失量情况;针对保护性耕作的特点,考虑到残茬覆盖对土壤含水量和地表粗糙度的影响;通过田间风蚀测定数据的验证,证明所建立的保护性耕作风蚀模型的模拟值与实测值比较吻合。     

耕作地表土块状况及其对近地表风场的影响

为深入理解非可蚀性土块吸收风能、降低侵蚀力的机制,利用野外风速资料,对半干旱区农田传统耕作模式下犁耕、耙耱及抹平等的地表土块大小、土壤表面粗糙度、近地表风速及空气动力学特征进行了研究。结果表明,犁耕后农田土块长、宽、高均在15 cm以上,盖度为27.67%,耙耱、抹平后土块大小和盖度显著降低,抹平地表土块盖度仅为2.13%;土块的破碎导致土壤表面粗糙度降低,近地表风速增大;与犁耕地表比较,耙耱后土壤表面粗糙度降低34%~64%,抹平后降低幅度甚至在90%以上;耙耱抹平后地表以上0.5 m高度内风速显著增大,空气动力学粗糙度由1.1 cm降低至0.05 cm,侵蚀力增强。因此认为,合理选择犁耕、耙耱和抹平的时间对农田风蚀防治有实际意义。     

河北坝上风蚀对农田土壤肥力水平影响研究

河北坝上地区风多风大,冬春季节降水少,使得大片农田长期处于强烈的风蚀之中.由于地表土壤养分的大量流失,农田土壤生产能力下降,导致荒漠化进程加剧.针对传统和保护性耕作农田土壤及风蚀物养分的变化,研究分析了土壤的风蚀和有机物及养分衰减的定量关系及其衰减的机理.结果表明:风蚀过程是农田土壤退化的重要路径,可以通过风蚀物中有机质和养分的含量估算农田土壤的有机质和养分的损失量.土壤风蚀过程中,保护性耕作比传统耕作可以减少风蚀量62.56%.有机质损失减少31.05%,全氮损失减少29.15%,全磷损失减少32.25%,全钾损失减少66.11%;有机质及养分主要集中在细微的土壤颗粒之中.风蚀对土壤营养物质及有机质的流失高于土壤的流失,风蚀是土壤退化的重要原因,恶化环境的同时造成了严重的经济损失.可以采用保护性耕作技术防止农田沙漠化和提高作物产量.     

保护性耕作农田风沙流空间分布规律研究

为了解保护性耕作农田风沙流的空间分布规律,对保护性耕作农田进行了野外风洞原位风蚀测试.结果表明:保护性耕作农田在不同风速下各高度的风沙流水平分布符合三次多项式规律,经过27行残茬、5.5 m的水平距离风沙流基本达到了平衡稳定状态;在垂直方向上风沙流分布符合高阶多项式规律,具有与砾石戈壁地表输沙量垂直分布极为相似的"象鼻"效应.试验还发现保护性耕作农田风沙流主要活动在近地表40 cm高度以下范围,占到风蚀物总质量的90%左右.     

中国北方农牧交错区夏季土壤风蚀研究——以河北丰宁县大滩乡二道河为例

土壤风蚀与风速、土壤粒径组成和地表的植被盖度有关 ,在农牧交错区 ,夏季存在着风蚀风速 ,由于植被盖度的增大 ,减缓了夏季风蚀现象的发生。所以 ,降低放牧强度 ,保持一定的植被盖度 ,不但能阻止夏季风蚀现象的发生 ,而且对来年春季的生态状况有较大影响。     

华北农田冬绿肥覆盖的抗风蚀研究

研究华北农田不同冬绿肥覆盖对农田土壤风蚀损失量的防治效果,并确定其最佳覆盖模式。结果表明:冬绿肥覆盖与冬闲相比,地表覆盖度、粗糙度增大,表层含水率提高,有机碳含量增加,土壤物理稳定性指数上升;5种冬绿肥覆盖模式可以不同程度减小土壤风蚀,风蚀量由大到小依次为:冬闲>草木樨>黑麦草>冬油菜>二月兰>毛苕子;综合看,冬油菜、毛苕子和二月兰覆盖的抗风蚀能力较强;风蚀大小与地表覆盖度、粗糙度、土壤有机碳含量、物理稳定性指数相关系数较高,而与土壤含水量相关系数较小。     

土壤风蚀量随风速的变化规律研究

使用野外风洞作为风蚀研究的试验手段,通过农田土壤、沙及生土的风洞试验研究发现,农田土壤的风蚀量随风速呈指数函数变化,沙及生土的风蚀量随风速呈幂函数变化。试验研究还表明,农田土壤的风蚀量与表土层(3cm)的含水量呈显著负相关,沙的风蚀量与含水量的相关性不显著。风蚀导致土壤中的细颗粒成分大量损失,这是土壤颗粒粗化的原因所在。     

Research on wind erosion processes and controlling factors based on wind tunnel test and 3D laser scanning technology

The study of wind erosion processes is of great importance to the prevention and control of soil wind erosion. In this study, three structurally intact soil samples were collected from the steppe of Inner Mongolia Autonomous Region, China and placed in a wind tunnel where they were subjected to six different wind speeds (10, 15, 17, 20, 25, and 30 m/s) to simulate wind erosion in the wind tunnel. After each test, the soil surfaces were scanned by a 3D laser scanner to create a high-resolution Digital Elevation Model (DEM), and the changes in wind erosion mass and microtopography were quantified. Based on this, we performed further analysis of wind erosion-controlling factors. The study results showed that the average measurement error between the 3D laser scanning method and weighing method was 6.23% for the three undisturbed soil samples. With increasing wind speed, the microtopography on the undisturbed soil surface first became smooth, and then fine stripes and pits gradually developed. In the initial stage of wind erosion processes, the ability of the soil to resist wind erosion was mainly affected by the soil hardness. In the late stage of wind erosion processes, the degree of soil erosion was mainly affected by soil organic matter and CaCO₃ content. The results of this study are expected to provide a theoretical basis for soil wind erosion control and promote the application of 3D laser scanners in wind erosion monitoring.     

沙地农业开发利用早期土壤风蚀的初步研究—以山东禹城为例

沙地农业开发利用，去除原有的植被，扰动了土体。在最初几年，土壤风蚀量不仅没有降低，而且明显增加。本文就产生土壤风蚀原因进行了分析，并对新开辟沙地的风蚀季相，以及高坑旱作型，灌溉型，流沙型，低温型土壤风蚀年际变化，进行了土壤风蚀量，风沙流结构的研究，对开发早期的不同类型的土壤风蚀，提出了不同的防治措施。     

Application of a new wind driving force model in soil wind erosion area of northern China

The shear stress generated by the wind on the land surface is the driving force that results in the wind erosion of the soil. It is an independent factor influencing soil wind erosion. The factors related to wind erosivity, known as submodels, mainly include the weather factor(WF) in revised wind erosion equation(RWEQ), the erosion submodel(ES) in wind erosion prediction system(WEPS), as well as the drift potential(DP) in wind energy environmental assessment. However, the essential factors of WF and ES contain wind, soil characteristics and surface coverings, which therefore results in the interdependence between WF or ES and other factors(e.g., soil erodible factor) in soil erosion models. Considering that DP is a relative indicator of the wind energy environment and does not have the value of expressing wind to induce shear stress on the surface. Therefore, a new factor is needed to express accurately wind erosivity. Based on the theoretical basis that the soil loss by wind erosion(Q) is proportional to the shear stress of the wind on the soil surface, a new model of wind driving force(WDF) was established, which expresses the potential capacity of wind to drive soil mass in per unit area and a period of time. Through the calculations in the typical area, the WDF, WF and DP are compared and analyzed from the theoretical basis, construction goal, problem-solving ability and typical area application; the spatial distribution of soil wind erosion intensity was concurrently compared with the spatial distributions of the WDF, WF and DP values in the typical area. The results indicate that the WDF is better to reflect the potential capacity of wind erosivity than WF and DP, and that the WDF model is a good model with universal applicability and can be logically incorporated into the soil wind erosion models.     

An experimental study on the influences of water erosion on wind erosion in arid and semi-arid regions

Complex erosion by wind and water causes serious harm in arid and semi-arid regions. The interaction mechanisms between water erosion and wind erosion is the key to further our understanding of the complex erosion. Therefore, in-depth understandings of the influences of water erosion on wind erosion is needed. This research used a wind tunnel and two rainfall simulators to investigate the influences of water erosion on succeeding wind erosion. The wind erosion measurements before and after water erosion were run on semi-fixed aeolian sandy soil configured with three slopes(5°, 10° and 15°), six wind speeds(0, 9, 11, 13, 15 and 20 m/s), and five rainfall intensities(0, 30, 45, 60 and 75 mm/h). Results showed that water erosion generally restrained the succeeding wind erosion. At a same slope, the restraining effects decreased as rainfall intensity increased, which decreased from 70.63% to 50.20% with rainfall intensity increased from 30 to 75 mm/h. Rills shaped by water erosion could weaken the restraining effects at wind speed exceeding 15 m/s mainly by cutting through the fine grain layer, exposing the sand layer prone to wind erosion to airflow. In addition, the restraining effects varied greatly among different soil types. The restraining effects of rainfall on the succeeding wind erosion depend on the formation of a coarsening layer with a crust and a compact fine grain layer after rainfall. The findings can deepen the understanding of the complex erosion and provide scientific basis for regional soil and water conservation in arid and semi-arid regions.     

A field investigation of wind erosion in the farming–pastoral ecotone of northern China using a portable wind tunnel: a case study in Yanchi County

The farming–pastoral ecotone in northern China is an extremely fragile ecological zone where wind erosion of cropland and rangeland is easy to occur. In this study, using a portable wind tunnel as a wind simulator, we conducted field simulated wind erosion experiments combined with laboratory analysis to investigate wind erosion of soils in trampled rangeland, non-tilled cropland and tilled cropland in Yanchi County, China. The results showed that compared with rangeland, the cropland had a higher soil water holding capacity and lower soil bulk density. The wind erosion rate of trampled rangeland was much higher than those of non-tilled cropland and tilled cropland. For cropland, the wind erosion rate of the soil after tilling was surprisingly less than that of the soil before tilling. With increasing of wind speed, the volume mean diameter of the eroded sediment collected by the trough in the wind tunnel generally increased while the clay and silt content decreased for all soils. The temporal variation in wind erosion of the trampled rangeland indicated that particle entrainment and dust emission decreased exponentially with erosion time through the successive wind erosion events due to the exhaustion of erodible particles.     

土壤风蚀对表层土壤粒度特征的影响

土壤风蚀是一种严重的环境问题。文中选择我国西北干旱及半干旱区,风蚀严重的盐池县风沙土地为研究对象,利用Marven2000粒度分析仪对不同风蚀强度的表层土壤粒度进行分析,探讨土壤风蚀过程对地表粒度的影响,研究表明:随着风蚀程度的增加,表层土壤粒度逐渐变粗,由灌丛-推平耕地-草地-吹蚀地,地表中的细沙,粉沙和粘土的含量逐渐降低,而中沙和粗沙的含量逐渐增加。灌丛表面以细沙为主,占34.9%;推平耕地和草地以中沙为主,占32.7和39.1%;吹蚀地以粗沙为主,占44.2%;土壤平均粒径逐渐变粗,分别为2.48,2.08,1.91,1.12φ。土壤风蚀过程,地表的细沙,粉沙和粘土大量损失,灌丛的细沙,粉沙和粘土分别占34.86,20.01和10.98%,但在严重风蚀的吹蚀地,细沙,粉沙和粘土仅占6.09,3.72和2.52%。由此可见,土壤风蚀造成地表细颗粒物质损失,形成沙漠化土地。不同地表沙粒的分维数不同,随平均粒径增加,分维数总体降低。