基于风蚀模型的准东地区土壤风蚀研究

文中选取准噶尔盆地东部(准东)为研究区,以土地利用类型、气象数据为基础,结合实地监测与调查,基于中科院寒区旱区环境与工程研究所的大田推广模型,定量计算各类地表在不同植被和风力条件下的土壤风蚀模数,分析准东地区土壤风蚀状况。结果表明:准东地区土壤风蚀模数呈现未利用地(风蚀模数6456.17t·km~(-2)·a~(-1))>林草地(风蚀模数3437.32t·km~(-2)·a~(-1))>耕地(风蚀模数758.71t·km~(-2)·a~(-1));土壤风蚀主要发生月份为4月和5月,占全年风蚀量的52%。模型模拟的准东地区年风蚀总量达10194.28万t,平均风蚀模数4571.43t·km~(-2)·a~(-1)。为验证模型模拟的准确性,用测钎法实测准东地区土壤风蚀模数,模型模拟值与实测之间的误差分析表明模型的精确性达84%以上,证明该模型可用于该区域土壤风蚀监测。     

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。     

土壤风蚀研究进展与评述

按照时间顺序，分阶段论述了国内外风蚀研究的概况及成果，系统地总结与评述了国内外土壤风蚀研究的进展，指出把土壤风蚀研究与农田耕作制度的研究结合起来，将是以后研究的重要方向。     

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。     

内蒙古京津风沙源治理工程土壤风蚀控制效益研究

2000—2013年内蒙古风沙源治理工程区风蚀模数整体呈现下降趋势,风蚀程度有所减轻。5个亚治理区风蚀模数差异较大,其中浑善达克沙地治理区风蚀模数最高,其他依次为科尔沁沙地南缘治理区﹥乌兰察布高平原退化草原、荒漠草原治理区﹥锡林郭勒高平原-乌珠穆沁沙地盆地退化草原治理区﹥华北北部丘陵山地水源涵养治理区。工程区土壤风蚀量明显减少,2001—2013年累计净减少1 370 446.65×104t,其中,乌兰察布高平原退化草原、荒漠草原治理区累计净减少风蚀量最大;其次为锡林郭勒高平原-乌珠穆沁沙地盆地退化草原治理区。风力是造成内蒙古风沙源工程区土壤侵蚀的最主要营力。2000—2013年,工程区风蚀模数与风蚀量的逐步降低说明,京津风沙源治理工程实施十余年以来,通过实施各类治理措施,工程区土壤风蚀得到初步控制,工程区生态状况趋向好转,随着森林资源总量与质量的提高,水土流失状况进一步改善,沙化土地治理初见成效。     

应用沙尘暴的气象资料测定土壤风蚀研究

<正> 自1984年以来,在西非、中东、美、澳等国,已开始应用沙尘暴的气象资料来描述大范围的土壤风蚀。研究证明,利用这些气象资料测定大范围的风蚀是有效的,但大量研究集中于沙尘暴频率这一指标。本文使用沙尘暴持续期和沙尘暴频率等综合性指标,对比研究了澳大利亚全国有沙尘暴记录的138个气象站(见图1)从1960年至1987年期间的沙尘暴情况,结果如下:     

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。     

以北方旱作农田为重点开展我国的土壤风蚀研究

本文在土壤风蚀倍受国际社会广泛关注的背景下，结合我国面临的实际情况，阐述了在北方旱作农田开展土壤风蚀研究的必要性。在评述国内外土壤风蚀研究进展和趋势的基础上，提出了我国拟开展的研究内容。针对我国土壤风蚀问题与研究现状，提出加快我国土壤风蚀研究的几点建议。     

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。     

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。     

灌木林优化配置格局对土壤风蚀的影响

低覆盖度时,灌木林的水平配置格局成为制约土壤风蚀的重要因素。以宁夏盐池县风沙区人工灌木林基地为试验区,研究了不同下垫面类型和不同配置格局的灌木沙障对风速、近地表输沙率和地表粗糙度的影响。结果表明:灌木林的防治土壤风蚀能力与灌木林的种类、高度和配置格局有直接关系:行带式配置能显著提高灌木林的防风效果,其中以沙柳林效果最佳;三行一带、平均高1.5m、行距1.5m、插深0.5m配置规格的沙柳沙障对地表土壤风蚀的控制效果最好,但防护范围限15倍带高以内;在行数一定的情况下,沙障高度越低,控制土壤风蚀能力越强。     

Impact factors of soil wind erosion in the center of Taklimakan Desert

The development and progress of soil wind erosion are influenced by the factors of climate,terrain,soil and vegetation,etc. This paper,taking Tazhong region,a town in the centre of the Taklimakan Desert,as an example and using comparative and quantitative methods,discussed the effects of climate,surface roughness(including vegetation cover) and surface soil properties on soil wind erosion. The results showed that the climate factor index C of annual wind erosion is 28.3,while the maximum of C is 13.9 in summer and it is only 0.7 in winter. The value of C has a very good exponential relationship with the wind speed. In Tazhong region,the surface roughness height is relatively small with a mean of 6.32 × 10-5 m,which is in favor of soil wind erosion. The wind erosion is further enhanced by its sandy soil types,soil particle size,lacking of vegetation and low soil moisture content. The present situation of soil wind erosion is the result of concurrent effects of climate,vegetation and surface soil properties.     

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.     

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.     

An experimental study on the influences of wind erosion on water erosion

In semi-arid regions, complex erosion resulted from a combination of wind and water actions has led to a massive soil loss and a comprehensive understanding of its mechanism is the first step toward prevention of the erosion. However, the mutual influences between wind erosion and water erosion have not been fully understood. This research used a wind tunnel and two rainfall simulators and simulated two rounds of alternations between wind erosion and water erosion(i.e., 1~(st) wind erosion–1~(st) water erosion and 2~(nd) wind erosion–2~(nd) water erosion) on three slopes(5°, 10°, and 15°) with six wind speeds(0, 9, 11, 13, 15, and 20 m/s) and five rainfall intensities(0, 30, 45, 60, and 75 mm/h). The objective was to analyze the influences of wind erosion on succeeding water erosion. Results showed that the effects of wind erosion on water erosion were not the same in the two rounds of tests. In the 1~(st) round of tests, wind erosion first restrained and then intensified water erosion mostly because the blocking effect of wind-sculpted micro-topography on surface flow was weakened with the increase in slope. In the 2~(nd) round of tests, wind erosion intensified water erosion on beds with no rills at gentle slopes and low rainfall intensities or with large-size rills at steep slopes and high rainfall intensities. Wind erosion restrained water erosion on beds with small rills at moderate slopes and moderate rainfall intensities. The effects were mainly related to the fine grain layer, rills and slope of the original bed in the 2~(nd) round of tests. The findings can deepen our understanding of complex erosion resulted from a combination of wind and water actions and provide scientific references to regional soil and water conservation.     

小麦留茬对陕北农田风蚀影响的室内风洞模拟

作为风蚀区主要保护性耕作措施之一,秸秆留茬覆盖可以通过增加地表粗糙度(Z0)减少近地表风速和侵蚀动力,并缩短风蚀颗粒的搬运距离和搬运高度,从而减少地表风蚀量.本研究采用室内模拟风洞实验,测定并分析了陕北2种主要土壤类型(风沙土和黄绵土)在4个风速、3种小麦留茬高度和2种留茬行距处理下土壤风蚀强度和在0～60 cm风洞断...     

气候变化对河北坝上不留茬农田土壤风蚀扬尘排放速率的影响

基于全球气候模式NorESM1-M产生的RCP2.6、RCP4.5、RCP6.0和RCP8.5气候变化情景数据,利用国家原环境保护部推荐的土壤风蚀扬尘计算方法,模拟分析了未来气候变化对河北坝上砂粘壤土、粘壤土、壤粘土、砂壤土、砂粘土和风沙土不留茬农田土壤风蚀扬尘总可悬浮颗粒物（Total suspended particle, TSP）、 PM₁₀和PM_2.5的季节和年排放速率影响。结果显示：气候变化影响下坝上地区气温上升,年降水量和风速波动较大,不同情景下变化趋势不同。RCP2.6、RCP4.5、RCP6.0和RCP8.5情景与基准情景下比较,不同土壤风蚀扬尘TSP、PM₁₀和PM_2.5季节排放速率在春季分别高15%、47%、28%和46%,夏季分别高1%、14%、3%和7%,秋季分别高17%、54%、45%和38%,冬季分别低36%、42%、39%和44%。在RCP2.6、RCP4.5、RCP6.0和RCP8.5情景下与基准情景下比较,按月排放累加计算,各土壤风蚀扬尘TSP、PM_10<...