• <tr id="yyy80"></tr>
  • <sup id="yyy80"></sup>
  • <tfoot id="yyy80"><noscript id="yyy80"></noscript></tfoot>
  • 99热精品在线国产_美女午夜性视频免费_国产精品国产高清国产av_av欧美777_自拍偷自拍亚洲精品老妇_亚洲熟女精品中文字幕_www日本黄色视频网_国产精品野战在线观看 ?

    Study on Physical Properties and Related Spectral Characteristics of Composited Soil with Different Ratio of Feldspathic Sandstone and Sand

    2015-01-18 02:50:12JuanLIJichangHAN
    Agricultural Science & Technology 2015年8期
    關(guān)鍵詞:毛烏素王濤沙地

    Juan LI,Jichang HAN

    1.Shaanxi Province Land Engineering Construction Group,Xi’an 710075,China;

    2.College of Forestry,Northwest A&F University,Yangling 712100,China;

    3.Key Laboratory of Degraded and Unused Land Consolidation Engineering,the Ministry of Land and Resources of China,Xi’an 710075,China

    Responsible editor:Yong XU Responsible proofreader:Xiaoyan WU

    Population increase and environmental damage make the global desertification degree become more and more serious,agricultural arable land resources face critical shortage,and the sustainable development of agriculture severely restricted.How to increase the area of arable land and improve land utilization has become the focus problem of economic development in the world today[1-4].Many scholars have being engaged in the research of the agricultural in desertified region,and strive to explore soil desertification control measures and ways to increase arable land with the aim to solve the shortage of land resources and desertification expansion and ease the pressure of land resources caused by population increase and social development[5-7].

    The southern margin of Maowusu Sandyland is located in the west farming-pastoral zone in north China,which belongs to the typical multi-level transition zone in geology and has weak ecotope,making it one of the area with most serious desertification in north China where the contradiction between people and land is very outstanding.Since 1987 when large-scale management of Maowusu Sandyland began,comprehensive treatment has been conducted to this area through the measures of afforestation and grass breeding to seal sand,ecological restoration,chemistry,physics,and adjusting measures to differing conditions[8-12],which have got certain achievements,but it fails to change the trend of desertification fundamentally.

    In view of resources,feldspathic sandstone and sand are the 2 most important resources in Maowusu Sandyland.The research results of YIN et al.[13],LI et al.[14]and WANG et al.[15]show edthat the mass fraction of chemical stable components in feldpathic sandstone reached 84.9%,and most of feldpathic sandstone existed in the form of between parent material and soil.However,feldspathic sandstone tended to become cement in dry status,and the volume-weight was usually 1.50-1.55 g/cm3,which greatly affected its permeability,air permeability and the crop roots stretching.When encountering water,the feldspathic sandstone would expand rapidly with the total porosity reaching up to 45.91%,and because of its good water retaining property,it can be used as water retaining material; with no structure,aeolian sandy soil could keep good water permeability under wet and dry conditions,but it has poor water retaining property.Therefore,the two were complementary to each other,and the alternative distribution of the two in the Maowusu Sandyland could generate interaction after mixing.Through the study on the interactions in the land resources of the feldspathic sandstone area,it could improve the physical and chemical properties,which could realize the reclamation of Maowusu Sandyland[16].In this study,based on field plot experiment and laboratory analysis,different proportions of feldspathic sandstone and sand were mixed into composited soil,and the composited soil texture,soil water storageand related spectral characteristic changes were analyzed to screen out the optimal mixture ratios of feldspathic sandstone and sand with the aim to provide scientific basis for the agricultural planting in Maowusu Sandyland by using composited soil technology in large-scale.

    Materials and Methods

    General situation of the test station

    Located in Chuyuan Village,Ducun County,Fuping Town,Weinan City,Shaanxi Province(109°11′30″ E,34°42′11″ N),the test place belonged to warm temperate semi humid climate zone,with the characteristics of the following:average annual rainfall of 472.97 mm,rainfall in July to September accounting for 49% of the total,annual evaporation amount of 1 000-1 300 mm,frost-free season of 225 d,annual average temperature of 13.4℃,summer maximum temperature of 41.8 ℃,winter minimum temperature of -22 ℃,annual total light radiation amount of 12.39 - 127.8 kca/cm2,and the climatic conditions could meet the needs of crop growth.

    Test design

    The trial was carried out from September 2010 to June 2013.In order to simulate the land conditions with the mixture of feldspathic sandstone and sand in the Maowusu Sandyland of the project experimental area,the thickness of the filling matrix in the test region was 70 cm (crop tillage layer generally was about 30 cm).The soil layers of this test were designed as follows:topsoil of 0-30 cm was the mixture of feldspathic sandstone(or loess)and sand,soil layer of 30 -70 was completely filled with sand,and both the feldspathic sandstone and sand came from the Dajihan Village,Xiaojihan County,Yuyang District,Yuyang.The mixture volume ratio of 1:2 of feldspathic sandstone and sand was the turning point for the decrease of saturated hydraulic conductivity of the mixture soil becoming slow.When the mixing ratio increased,the saturated hydraulic conductivity became decreased gently[17].Therefore,4 treatments were set in this test with the mixing volume ratio of feldspathic sandstone and sand of 1:1 (C1),1:2(C2) and 1:5 (C3),and the CK used loess soil and sand.The test plot area was 2 m × 2 m = 4 m2,and with there replicates,there were 12 test plots in total,which were laid out in a line from south to north.

    Test materialsThe tested materials were wheat Xiaoyan 22.

    Test plot managementThe fertilization amounts of all test plots were as follows:N of 255 kg/hm2,P2O5of 180 kg/hm2,K2O of 90 kg/hm2.The applied nitrogen fertilizer,phosphate fertilizer,potash fertilizer were urea,diammonium phosphate and potassium chloride,and all fertilizers were base fertilizer.

    Before sowing winter wheat,the application amount of the fertilizers was calculated according to the plot area,which was applied through manual work.The soil should be prepared to make it flat and the fertilizers evenly distributed.The wheat was sown manually in line with the sowing amount of 150 kg/hm2and row spacing of 20 cm.No fertilizer was applied during the growth period of wheat,and before tilllering,the wheat was irrigated once.The irrigation amount of the 12 test plots was the same,and the other management was the same as that of the local fields.

    The wheat sowing time of the three planting seasons were September 18,2010,Septermeber 20,2011 and September 24,2012,and the corresponding harvest time was June 8,2011,June 10,2012 and June 5,2013.

    Testing items and methods

    Measurement of soil moistureAfter the harvest of winter wheat,the earth boring auger was used to take soil samples,which was used to test the soil moisture content in the depth of 0 -60 cm by using oven drying method,and soil sampling interval was 10 cm.

    Measurement of soil textureAfter the wheat harvest,soil samples in the depth of 0-30 cm were collected,from which the coarse roots and small stones were removed.Quartering method was used to take the testing soil samples,which were then dried naturally and meshed by the 0.149 mm mesh.Master-sizer 2000 was used to determine the soil texture,and according to the United States agricultural soil texture classification system of the US[18],the soil grains were classified into sand (grain diameter of 2 -0.05 mm),silt(grain diameter of 0.05-0.002 mm)and clay (grain diameter of smaller than 0.002 mm).

    Determination of wheat spectraIn 2013,5 representative wheat plants were selected from each test plot during the winter wheat jointing stage and filling stage in sunny days to determine the canopy reflectance at 10:30-13:30 using ASD FiedlSpec4 high spectrometer (wavelength range of 350-2 500 nm,spectral sampling interval of about 1.5 nm,spectral resolution of 3.5 nm with the standard ASD spectrometer configuration of 7.5°field angle).During the determination,the sensor probe was vertically downward at about 10 cm above the top of the leaf.Every 10 spectral samples was a group,and each time 2 groups were determined,and the mean value was used as the canopy spectral reflectance of each plot.In order to reduce the influence of weather change,standard blank was corrected before and after the measurement of each group.

    Determination of soil spectraIn 2013,3 spots were selected from each test plot after winter wheat harvest in sunny days to determine the soil spectral reflectance at 10:30-13:30 using ASD FiedlSpec4 high spectrometer(same parameters as above).During the determination,the sensor probe was vertically downward at about 15 cm above the soil.Every 10 spectral samples was a group,and the mean value was used as the soil spectral reflectance of each plot.In order to reduce the influence of weather change,standard blank was corrected before and after the measurement of each group.

    Data calculation and statistical analysis

    W=Wi×Di×Hi×10/100

    Where,Wis soil water storage;Wi is the soil water content of the ithlayer;Dit is the soil bulk density of the ith layer;Hiis the soil layer thickness of the ith layer s.

    Microsoft Excel 2010 was used to process all data,charts,and graphs,and SPSS (PASW Statistics 18) was used for the statistical analysis.Duncan new repolarization difference method (SSR) was used for multiple comparisons.

    Results and Analysis

    Change of soil texture of composited soil in 0-30 cm soil layer

    Due to the influence of soil fertility,climate,crop root and biological activities,soil texture would also change with the increase of planting year,including the content of sand,silt and clay.After the winter wheat harvest in 2011,2012 and 2013,in the composited soil with different proportions of feldspathic sandstone (or loess) and sand,the changes of soil grain levels in 0-30 cm soil depth (Fig.1,2,3 and 4) indicated that with the increase of planting year,all composited soil mixed with feldspathic sandstone and sand showed decrease in the proportion of and and incrase of silt;the composited soil mixed with loess and sand showed decrease in clay and increase in sand.

    After the wheat harvest in 2011,compared with other composited soils,treatment CK showed the highest clay content in the depth of 0-30 cm,and the content of clay increased with the increase of soil depth,while the content of both silt and sand decreased(Fig.1a),which was mainly because of the interactions between the root system and soil fertility during the early stage of crop planting,which could form cementation between the soil layers.With the increase of planting year,the proportion of silt increased in every treatment soil,and after wheat harvest in 2013,the soil silt content of treatment CK in the depth of 0-30 cm reached up to 26.07%,which was 73.49% and 47.25% higher than that in 2011 and 2012.The soil texture composited with feldsapthic sandstone and sand showed uniform trend the content of sand decreased significantly,while the content of silt increased and gathered on surface soil,and the content of clay showed no significant change (Fig.2,3 and 4).After wheat harvest in 2013,treatment C1,C2 and C3 in soil depth of 0-30 cm showed that the content of sand decreased by 13.41%,12.73% and 8.45%than that of 2011;in the 3 treatments,the content of sand increased with the increase of the proportion of sand,respectively,69.21%,76.69%and 78.94%,and all treatments showed significant differences (P<0.05);in all treatments,the changes of silt contents were the same as that of sand that treatment C1 in the soil depth of 0-30 cm showed the average silt content of 24.99%,which was 6.27% and 8.25% higher than that of the treatment of C2 and C3,and all treatments were significantly different from each other (P<0.05).In the soil depth of 0-15 cm of treatment C1,sand gathered together reaching up to 34,22,which might cause greater soil surface evaporation,resulting in water loss.After wheat harvest in 2013,all treatments showed that clay content decreased with the increase of soil layer depth and decreased with the increase of the mixing proportion of sand in the soil.In the soil depth of 0-30 cm of treatment C1,C2 and C3,the average clay contents were 5.80%,4.70% and 4.15%,respectively,and all treatments were significantly different from each other(P <0.05).

    To sum up,after wheat harvest in 2013,treatment CK along the soil depth of 0-30 cm showed the average clay content decreased by 62.60% to that of 2011,the fast decrease of clay content increased soil porosity,which was easy to accelerate water evaporation and reduce effective utilization rate.Treatment C1 along the soil depth of 0-15 cm showed the accumulation of silt,which increased the surface soil porosity,making it easy to cause high soil water loss rate,which was not favorable to water and fertilizer retention.In treatment C3 along the soil depth of 0=30 cm,the average sand content was 79.17%,which was not favorable for water conservation.Treatment C2 along the soil depth of 0-30 cm showed coordinated proportions of clay and silt,which was suitable for crop production and soil water conservation,ensuring the growth and development of winter wheat.

    Moisture storage of composited soil in 0-60 cm soil layer

    After winter wheat harvest in 2011,2012 and 2013,the water storage in the soil layer of 0-60 (Table1)showed that the annual water storage amount of treatment C2 was higher than hat of the other treatments,indicating that the soil water storage of composted soil in 0-60 cm soil layer would decrease no matter the proportions of feldspathic sandstone was too low or too high.In 2011,the soil water amount of CK and C1 in 0-60 cm soil layer showed significant differences from the other treatments (P <0.05),and the water storage amounts in 0-60 cm soil layer were in the order of C2 >C3 >C1 >CK.The soil water storage of C2 in 0-60 cm soil layer was 20.31%,7.97%and 1.79%higher than that of CK,C1 and C3.In 2013,the soil water storage of C2 in 0-60 cm soil layer showed significant difference with the other treatments (P <0.05),and the order was the same as that in 2011.The soil water storage of C2 in 0-60 cm soil layer was 20.05%,18.90% and 6.62% higher than that of CK,C1 and C3.In 2013,the soil water storage of C2 in 0-60 cm soil layer was 19.06%,8.59%and 3.62%higher than that of CK,C1 and C3,respectively.

    The average water storage amount of treatment CK,C1,C2 and C3 in 0-60 cm soil layer was 47.32,51.46,57.42 and 55.26 mm,respectively,indicating that treatment C2 was most beneficial to soil water conservation,which could better ensure the smooth germination and growth of wheat seeds.

    Spectral characteristics of wheat in different growth stages

    The canopy reflection spectral curves at the different stages of wheat growth in the composited soil with different proportions of feldspathic sandstone and sand were also different.In 2013,the spectral reflection curve characters were similar for all treatment of winter wheat at the jointing stage and filling stage along the fullwave band (350-2 500 nm),and the reflectance was higher in the jointing stage than the filling stage (Fig.5a and 6a).For all treatments,the canopy reflection spectra in the visible region(400-1 000 nm)first increased gradually and then decreased,and then increased greatly and then decreased(Fig.5b and 6b).The reflection peak was found around 550 nm,a part of green light wave band,and when the light band was over 800 nm,the reflectance tended to be stable,forming a reflection platform.Treatment C2 showed the highest canopy reflectance at the jointing stage of 0.21%,which was significantly different from the other treatments (P <0.05),indicating that under treatment C2,the crops showed good growth conditions,and the overall difference in leaves was small,which was mainly because during this period,the wheat canopy reflectance was greatly influenced by the soil reflectance,and the effect of soil reflectance on canopy reflectance was smaller when the wheat grew well.At the wavelength region of 680-820 nm,the wheat canopy reflectance of all treatments presented negative correlation with the wavelength in jointing stage,that is,with the increase of wavelength,the reflectance decreased.At the filling stage,the wheat canopy reflectance of all treatments was in the order of C3 >C1 >CK >C2,which may because the effect of soil reflectance on wheat canopy reflectance was small in this stage,which was mainly related with the chlorophyll content in the leaf.Treatment C2 showed the lowest reflectance at this stage,indicating that under treatment C2,the crops showed good growth conditions,and the content of canopy chlorophyll content was high.

    Soil spectral characteristics

    Different soil texture showed different light reflectance.In 2013,all treatments showed similar spectral curve characters at the wavelength of 350-1 750 nm after winter wheat harvest(Fig.7).The relative reflectance of soil increased during 350-1 750 nm wave length along with the increase of sand proportion.Under the treatment CK,C1,C2 and C3,the soil average reflectance was 0.317%,0.303%,0.321% and 0.339%,respectively.At the 350-750 nm band,for treatment CK,C1,C2 and C3,the soil spectral reflectance (y) and wave length (x)presented highly correlated relationship,and the correlation equations were as follows:y = 0.187 1ln (x) -0.979 4,y = 0.158 7 ln (x) - 0.801 2,y= 0.177 1ln (x) - 0.910 8 and y =0.184 5ln(x)-0.944 5.And the correlation coefficient was 0.653,0.553,0.653 and 0.672,respectively.At the wave length of 1 350-1 450 nm band,soil reflectance had an obvious peak,but it was not suitable for data analysis,for the wave length was mainly caused by water vapor absorption caused,which was very sensitive to water[19].

    Discussion

    As an important physical characteristic,texture is subject to the influence of many factors like parent material,climate,topography,groundwater hydrology and so on.,making it present certain regularity and constitutive property in special distribution.Soil texture affects the migration,distribu-tion and utilization efficiency of soil nutrients,and,therefore,research on its spatial variation is of great significance to soil improvement,irrigation,fertilization and eco agricultural regionalization[18].The test results of this study showed that after the winter wheat harvest in 2011,2012 and 2013,in the composited soils with different mixing proportions of feldspathic sandstone(loess)and sand in 0-30 cm soil layer,with the increase of planting year,treatment C1,C2 and C3 showed decrease in sand but increase in silt,while treatment CK showed decrease in clay but increase in sand.After planting crops for 3 seasons,the sand content in 0-30 cm soil layer of treatment CK showed an increase of 43.44% to that of the early stage; the sand content in 0-30 cm soil layer of treatment C1,C2 and C3 decreased by 13.41%,12.73% and 8.45%,respectively,and silt content increased by 14.53%,13.16% and 8.82%,respectively,which presenting significant differences among all treatments (P <0.05).Soil texture directly affects soil water retention,permeability and retention.The test results of this study showed that with the increase of planting year,the soil texture was better in ventilation and water permeability.The average sand,silt and clay content in the 3 planting seasons of treatment C2 in 0-30 cm soil layer was respectively 76.69%and 18.72%and 4.70%,which was more suitable for plant growth.Due to differences in soil texture,treatment CK,C1,C2 and C3 showed significant difference in water storage in 0-60 cm soil layer,which first increased with the increase of sand proportions,and then decreased with the increase of sand proportions after treatment C2 showed the maximum water storage.The average water storage in 0-60 cm soil layer of treatment C2 was 57.42 mm.

    Table1 Soil water storage in 0-60 cm soil layer under different treatments(2011-2013)

    There have many studies on crop canopy characteristics but with different conclusions.The application of spectroscopy overcomes the disadvantage of time-consuming and damage to the crop,achieving efficient management and production[20].This study analyzed the canopy reflectance of winter wheat at jointing stage and filling stage in 2013,and the canopy reflectance of all treatments at the jointing stage was higher than that at the filling stage.The canopy reflectance of all treatments first increased and then decreased,and the reflection peak was found around 550 nm,a part of green light wave band.Treatment C2 showed the highest canopy reflectance at the jointing stage and lowest in the filling stage,which was mainly because with the advance of the growth period of wheat,the photosynthetic capacity increased,the influence of soil reflectance on canopy reflectance decreased,the absorption of visible light gradually increased,and the reflectance gradually decreased.The reason why the canopy reflectance at jointing stage higher than at filling stage was that the proportions of leaves with high chlorophyll content in the crop canopy of wheat decreased at the filling stage,while the proportions of wheat awns in canopy increased,which decreased the reflectance in near infrared region.In the mean time,the effects of diseases and pests on wheat became obvious at the filling stage,which could also decrease the reflectance[21-22].

    Soil spectral character is also affected by many factors like soil moisture,soil organic matter content,iron oxide,soil texture and so on.After three seasons of crops planting,the soil spectrum of each treatment was determined in 2013 after wheat harvest,and the results showed that all treatments had similar spectral characters at the 350 -1 750 nm wave length,and the soil spectral reflectance increased with the increase of sand proportions,which was mainly caused by the differences in soil texture.The increase in sand proportions would intensity the cementation and interaction between particles,which could increase the spectral reflectance.Bowers et al.[24]studied the effect of mechanical composition on the energy of soil reflection,and the results showed that soil spectral reflectance presented exponential growth with the soil particles becoming small,which was especially more obvious when the diameter of soil particles was less than 0.4 μm.The study of Alabbas et al.[25]found that soil clay content presented negative correlation with soil spectral reflectance,which was consistence with the results of this study that under treatments C1,C2 and C3,with the decrease of clay content in soil texture,the spectral reflectance increased.During 350-1 750 nm wave length,for treatment CK,C1,C2 and C3,the soil spectral reflectance(y)of different soils and wave length(x)showed good logarithmic relationship as follows:y = 0.187ln (x)-0.979,y=0.159ln(x)-0.801,y=0.177ln(x)-0.911 and y=0.185ln(x)-0.945.

    Composing feldspathic sandstone with sand according to different proportions could replace the traditional methods of soil improvement.Combining the complementarity of feldspathic sandstone and sand with scientific planting technology combination,the composited soil could be superior to the soil improved by traditional method to a certain extent,and experimental study shows that the mixing proportion of 1:2 can increase the soil moisture storage capacity,which is conducive to the growth of crops.This study only investigated the differences of soil texture,moisture and spectral characteristics,and further study is required to learn the the effects of other soil index and crop yield.

    [1]KONG DZ (孔德珍).The ecological economic principle for comprehensive development and management of Maowusu Sandland(毛烏素沙地綜合開發(fā)治理的經(jīng)濟(jì)學(xué)原則)[J].Pratacultural Science,1996,13(3):13-15.

    [2]ZHENG YR(鄭元潤),ZHANG XS(張新時).The diagnosis and optimal design of high efficient ecological economy system in Mowusu Sandland(毛烏素沙地高效生態(tài)經(jīng)濟(jì)復(fù)合系統(tǒng)診斷與優(yōu)化設(shè)計)[J].Acta Phytoecologica Sinica,1998,22(3):262-268.

    [3]WANG RD (王仁德),WU XX (吳曉旭).New pattern to control Maowusu Sandland(毛烏素沙地治理的新模式)[J].Research of Soil and Water Conservation,2009,16(5):176-180.

    [4]CAI YL(蔡運(yùn)龍),Barry S.Sensitivity and adaptation of Chinese agriculture under global climate change (全球氣候變化下中國農(nóng)業(yè)的脆弱性與適應(yīng)對策)[J].Acta Geographica Sinica,1996,51 (3):202-210.

    [5]CHEN YQ (陳瑜琦),LI XB (李秀彬).Structural change of agricultural land use intensity and its regional disparity in China (1980年以來中國耕地利用集約度的結(jié)構(gòu)特征)[J].Acta Geographica Sinica,2009,64(4):469-478.

    [6]CUI DC(崔讀昌).The possible influence of climate getting warmer on agricultural production in China (氣候變暖對我國農(nóng)業(yè)生產(chǎn)的影響與對策)[J].Chinese Journal of Agrometeorology,1992,13 (2):16-20.

    [7]LIU XQ (劉曉瓊),LIU YS (劉彥隨).Countermeasures on adjustment of regional industry structures under climate drying change (干旱化背景下區(qū)域產(chǎn)業(yè)發(fā)展適應(yīng)對策)[J].Progress in Geography,2006,25(5):86-93.

    [8]GAO GX(高國雄).In Maowusu Sandyland development zone vegetation at the beginning of construction technology research (毛烏素沙地能源開發(fā)區(qū)植被建設(shè)技術(shù)研究初報)[J].Journal of Soil and Water Conservation Research,2002,9(3):156-157.

    [9]SHI YC(石迎春),YE H(葉浩),HOU HB(侯宏冰),et al.The internal cause of erosion in “Pisha” sandstone area,southern inner Mongolia(內(nèi)蒙古南部砒砂巖侵蝕內(nèi)因分析)[J].Acta Geographica Sinica,2004,25(6):659-664.

    [10]HAN LW (韓麗文),LI ZH (李祝賀),SHAN XP(單學(xué)平),et al.Research on strategy for land desertification control(土地沙化與防沙治沙措施研究)[J].Research of Soil and Water Conservation,2005,12(5):210-213.

    [11]GUO J(郭堅),WANG T(王濤),XUE X(薛嫻),et al.The status and distribution of desertification in Maowusu Sandyland (毛烏素沙地荒漠化現(xiàn)狀及分布特征)[J].Research of Soil and Water Conservation,2006,13 (3),198-203.

    [12]WU W (吳薇).Desertification process and its controlling counter measures in Maowusu Sandyland in China (毛烏素沙地沙漠化過程及其整治對策)[J].Chinese Journal of Eco-Agriculture,2001,9(3):15-18.

    [13]YIN LQ (殷麗強(qiáng)),WANG T (王濤),LIANG Y (梁月).Study on soil hydrophysical properties of artificial seabuckthorn stands in arsenic sandstone area (砒砂巖地區(qū)沙棘人工林地土壤水分物理性質(zhì)研究)[J].The Global Seabuckthorn Research and Development,2008,6(1):9-12.

    [14]LI XL(李曉麗),SU Y(蘇雅),QI YH(齊曉華).The experimental analysis study of soft sandstone soil properties in the plateau hilly region(高原丘陵區(qū)砒砂巖土壤特性的實(shí)驗(yàn)分析研究)[J].Journal of Inner Mongolia Agricultural University,2011,32(1),315-318.

    [15]WANG YC(王愿昌),WU YH(吳永紅),KOU Q (寇權(quán)),et al.Definition of arsenic rock zone borderline and its classification (砒沙巖分布范圍界定與類型劃分)[J].Science of Soil and Water Conservation,2007,5(1):14-18.

    [16]WANG HY(王歡元),HAN JC(韓霽昌),LUO TL (羅林濤),et al.Regulatory role of sand in soil formation from soft rock and sand(砒砂巖與沙復(fù)配成土過程中沙的調(diào)控作用)[J].Chinese Journal of Soil Science,2014,45 (2),286-290.

    [17]WABG R(王銳),LIU WZ(劉文兆),LI Z(李志).Physical properties of soils along a 10 m deep soil profile in loess tableland (黃土塬區(qū)10 m 深剖面土壤物理性質(zhì)研究)[J].Acta Phytoecologica Sinica,2008,45(3):550-554.

    [18]HUANG CY(黃昌勇).Soil science(土壤學(xué))[M].Beijing:China Agriculture Press,2000,74-79.

    [19]CHEN Z (陳禎).Relationship model among water content,bulk density and reflectivity of different soil(不同土壤含水率體積質(zhì)量及光譜反射率的關(guān)系模型)[J].Transactions of the Chinese Society of Agricultural Engineering,2012,28(4):76-81.

    [20]TANG Y(唐延林),HUANG JF(黃敬峰),WANG XZ(王秀珍),et al.Comparison of the characteristics of hyperspectra and the red edge in rice,corn and cotton(水稻、玉米、棉花的高光譜及其紅邊特征比較)[J].Scientia Agricultra Sinica,2001,37(1):29-35.

    [21]PENG J (彭杰),ZHANG YZ (張楊珠),ZHOU Q(周清),et al.The progress on the relationship physics-chemistry properties with spectrum characteristic of the soil(去除有機(jī)質(zhì)對土壤光譜特性的影響)[J].Chinese Journal of Soil Science,2009,40(5):1204-1208.

    [22]SUN H(孫紅),LI MZ(李民贊),ZHAO Y(趙勇),et al.The spectral characteristics and chlorophyll content at winter wheat growth stages(冬小麥生長期光譜變化特征與葉綠素含量監(jiān)測研究)[J].Spectroscopy and Spectral Analysis,2010,10(1):192-196.

    [23]SONG WC(宋文沖),HU CS(胡春勝),CHENG YS (程一松),et al.Research advancement on crop nitrogen nutrition diagnosis(作物氮營養(yǎng)診斷方法研究進(jìn)展)[J].Chinese Journal of Soil Science,2006,4:370.

    [24]BOWERS S,HANKS RJ.Reflectance of radiant energy from soil[J].Soil Science,1965:130-138.

    [25]ALABBAS AH,SWAIN PH,BAUMGARDNER MF.Relating organic matter and clay congtent to multispectral radiance of soil [J].Soil Science,972,114(6):477-485.

    猜你喜歡
    毛烏素王濤沙地
    綿師學(xué)人
    ——王濤
    Transition to chaos in lid–driven square cavity flow?
    能鉆過柔軟沙地的蛇形機(jī)器人
    軍事文摘(2021年18期)2021-12-02 01:27:58
    毛烏素花海
    金秋(2021年8期)2021-07-27 02:10:48
    呼倫貝爾沙地實(shí)現(xiàn)良性逆轉(zhuǎn)
    沙地迷宮
    毛烏素
    毛烏素沙地砒砂巖與沙復(fù)配土壤顆粒組成動態(tài)變化特征
    風(fēng)滾草
    王濤作品
    18禁在线无遮挡免费观看视频| 极品教师在线视频| 男女啪啪激烈高潮av片| 欧美xxxx性猛交bbbb| 国产成人精品久久久久久| 久久久久久久亚洲中文字幕| 久久草成人影院| 蜜桃亚洲精品一区二区三区| 成人亚洲精品av一区二区| 国产精品久久视频播放| 亚洲成人一二三区av| 久久亚洲国产成人精品v| 久久久久久久久久久免费av| 国产伦精品一区二区三区视频9| 99热网站在线观看| 午夜免费激情av| 欧美高清性xxxxhd video| 国产 一区 欧美 日韩| 欧美 日韩 精品 国产| 国产 亚洲一区二区三区 | 国产人妻一区二区三区在| 最近手机中文字幕大全| 2021少妇久久久久久久久久久| 国产精品熟女久久久久浪| 久久久色成人| 舔av片在线| 亚洲欧美日韩卡通动漫| 免费看av在线观看网站| 人妻制服诱惑在线中文字幕| 欧美日韩精品成人综合77777| 成人漫画全彩无遮挡| 日韩亚洲欧美综合| 男人狂女人下面高潮的视频| 成人午夜高清在线视频| 午夜久久久久精精品| 亚洲人与动物交配视频| 建设人人有责人人尽责人人享有的 | av国产免费在线观看| 亚洲成人精品中文字幕电影| 国产不卡一卡二| 搡女人真爽免费视频火全软件| 久久久久久久久大av| 我的女老师完整版在线观看| 亚州av有码| 乱人视频在线观看| 久久草成人影院| 不卡视频在线观看欧美| av播播在线观看一区| 国产精品爽爽va在线观看网站| 久久精品夜色国产| 久久久久久久久久成人| 久久精品夜夜夜夜夜久久蜜豆| 一夜夜www| 亚洲精品456在线播放app| 国产午夜精品论理片| 久久久亚洲精品成人影院| 有码 亚洲区| 国产精品嫩草影院av在线观看| 国产单亲对白刺激| 欧美丝袜亚洲另类| 亚洲av二区三区四区| 99久久九九国产精品国产免费| 伦理电影大哥的女人| av在线蜜桃| 亚洲乱码一区二区免费版| 成人国产麻豆网| 精品久久国产蜜桃| 成人鲁丝片一二三区免费| 久久久久久久久久成人| 哪个播放器可以免费观看大片| 日本免费a在线| 成人鲁丝片一二三区免费| 十八禁网站网址无遮挡 | 久久精品夜夜夜夜夜久久蜜豆| 久久久a久久爽久久v久久| 亚洲欧美日韩东京热| 男人舔奶头视频| 麻豆国产97在线/欧美| 男人和女人高潮做爰伦理| 在线观看人妻少妇| 高清午夜精品一区二区三区| 国产精品久久久久久精品电影| 久久97久久精品| 精品一区二区三区视频在线| 男插女下体视频免费在线播放| 久久国内精品自在自线图片| 乱系列少妇在线播放| 久久精品久久久久久久性| 亚洲美女搞黄在线观看| 欧美成人午夜免费资源| 日日啪夜夜爽| av天堂中文字幕网| 日韩av免费高清视频| 能在线免费观看的黄片| 日韩,欧美,国产一区二区三区| 美女主播在线视频| 嫩草影院入口| 日韩电影二区| 晚上一个人看的免费电影| 天天一区二区日本电影三级| 最新中文字幕久久久久| 一级毛片我不卡| 丝袜喷水一区| 中文天堂在线官网| 亚洲精品久久午夜乱码| 中文字幕亚洲精品专区| 国内精品一区二区在线观看| 亚洲精品视频女| 免费高清在线观看视频在线观看| 午夜爱爱视频在线播放| 一本一本综合久久| 在线免费观看不下载黄p国产| 色尼玛亚洲综合影院| 伦精品一区二区三区| 欧美精品一区二区大全| 亚洲欧美成人综合另类久久久| av国产久精品久网站免费入址| 国产成人a区在线观看| av网站免费在线观看视频 | 国产精品美女特级片免费视频播放器| 国产又色又爽无遮挡免| 男女下面进入的视频免费午夜| videossex国产| 男女那种视频在线观看| 22中文网久久字幕| 国产精品女同一区二区软件| 精品一区二区三区视频在线| 亚洲精品日本国产第一区| 日韩欧美精品v在线| 久久99精品国语久久久| 国产精品人妻久久久影院| 超碰av人人做人人爽久久| 男人爽女人下面视频在线观看| 久久精品国产亚洲av天美| 在线播放无遮挡| 三级男女做爰猛烈吃奶摸视频| 偷拍熟女少妇极品色| 国产成人aa在线观看| 国产色婷婷99| 高清视频免费观看一区二区 | 免费av毛片视频| 久久99热这里只频精品6学生| 狂野欧美白嫩少妇大欣赏| 中文字幕免费在线视频6| 国产伦一二天堂av在线观看| 只有这里有精品99| 亚洲精品国产成人久久av| 99热6这里只有精品| 亚洲av电影不卡..在线观看| 18+在线观看网站| 99久久精品热视频| 亚洲在线自拍视频| 亚洲av在线观看美女高潮| 久久久久久久亚洲中文字幕| 免费观看av网站的网址| 国产一区二区在线观看日韩| 我要看日韩黄色一级片| 在线观看美女被高潮喷水网站| 麻豆av噜噜一区二区三区| 久久久a久久爽久久v久久| 久久鲁丝午夜福利片| 尾随美女入室| 久久久午夜欧美精品| 色哟哟·www| 国产av国产精品国产| 色视频www国产| 大又大粗又爽又黄少妇毛片口| 看十八女毛片水多多多| 精品人妻视频免费看| 男女国产视频网站| 51国产日韩欧美| av在线老鸭窝| 国产精品一区二区在线观看99 | 搞女人的毛片| 最近最新中文字幕大全电影3| 色5月婷婷丁香| 亚洲第一区二区三区不卡| 国产av在哪里看| 欧美+日韩+精品| 欧美人与善性xxx| 亚洲激情五月婷婷啪啪| 亚洲精品色激情综合| 欧美成人一区二区免费高清观看| 国产91av在线免费观看| 日韩国内少妇激情av| 亚洲av日韩在线播放| 美女国产视频在线观看| 国产一区二区亚洲精品在线观看| 1000部很黄的大片| 少妇被粗大猛烈的视频| 少妇人妻一区二区三区视频| 国内精品美女久久久久久| 日韩精品青青久久久久久| 国产亚洲91精品色在线| 一区二区三区乱码不卡18| 18禁动态无遮挡网站| 亚洲最大成人中文| av免费观看日本| 中国国产av一级| 亚洲美女搞黄在线观看| 日本与韩国留学比较| 六月丁香七月| 国产午夜精品一二区理论片| 国产精品一及| 精品99又大又爽又粗少妇毛片| 1000部很黄的大片| 日韩欧美精品免费久久| 亚洲欧美日韩东京热| 777米奇影视久久| 国产单亲对白刺激| av天堂中文字幕网| 日韩三级伦理在线观看| 亚洲最大成人手机在线| 久久久久久久亚洲中文字幕| 国产免费福利视频在线观看| 午夜激情久久久久久久| 最近的中文字幕免费完整| 日韩视频在线欧美| 国产精品国产三级专区第一集| 99九九线精品视频在线观看视频| 国产视频内射| 日本熟妇午夜| 久久久久精品久久久久真实原创| 久久久精品欧美日韩精品| 国产黄色视频一区二区在线观看| 国产在线男女| 亚洲激情五月婷婷啪啪| 一级毛片电影观看| 99热全是精品| 看免费成人av毛片| 舔av片在线| 极品少妇高潮喷水抽搐| 看非洲黑人一级黄片| 久久久久网色| 少妇的逼水好多| 欧美日韩一区二区视频在线观看视频在线 | 久久久久久久久久成人| 国产一级毛片七仙女欲春2| 日韩制服骚丝袜av| 日本爱情动作片www.在线观看| 麻豆乱淫一区二区| 97超碰精品成人国产| 久久99蜜桃精品久久| 国产综合精华液| 极品教师在线视频| 黄色日韩在线| 国产精品日韩av在线免费观看| 丝瓜视频免费看黄片| 亚洲精品久久久久久婷婷小说| 国产成人a∨麻豆精品| 午夜视频国产福利| 爱豆传媒免费全集在线观看| 尤物成人国产欧美一区二区三区| 久久精品夜夜夜夜夜久久蜜豆| 亚洲精品成人av观看孕妇| 女人久久www免费人成看片| 国产亚洲最大av| av黄色大香蕉| 婷婷六月久久综合丁香| 蜜桃亚洲精品一区二区三区| 亚洲精品,欧美精品| 好男人在线观看高清免费视频| 白带黄色成豆腐渣| 69人妻影院| 极品少妇高潮喷水抽搐| 又大又黄又爽视频免费| 国产人妻一区二区三区在| 在线a可以看的网站| 欧美性感艳星| 亚洲天堂国产精品一区在线| 久久精品国产自在天天线| 一级黄片播放器| 国产精品久久久久久久电影| 成人无遮挡网站| 一个人看视频在线观看www免费| 天堂√8在线中文| 亚洲精品一区蜜桃| 欧美bdsm另类| 亚洲精品456在线播放app| 日韩av不卡免费在线播放| 午夜福利视频1000在线观看| 欧美不卡视频在线免费观看| 免费看美女性在线毛片视频| 欧美高清成人免费视频www| 最新中文字幕久久久久| 亚洲精品456在线播放app| 男女边摸边吃奶| 亚洲最大成人手机在线| av.在线天堂| 大片免费播放器 马上看| 一个人看视频在线观看www免费| 久久久久久久午夜电影| av专区在线播放| 久久久久久伊人网av| 午夜福利成人在线免费观看| 国产 一区精品| 最近2019中文字幕mv第一页| 22中文网久久字幕| 国产精品美女特级片免费视频播放器| 国产v大片淫在线免费观看| 亚洲精品亚洲一区二区| 51国产日韩欧美| 身体一侧抽搐| 久久久色成人| 国产精品一区二区性色av| 丰满少妇做爰视频| 成人亚洲欧美一区二区av| 日日摸夜夜添夜夜爱| 午夜免费观看性视频| 菩萨蛮人人尽说江南好唐韦庄| a级毛色黄片| 国产男女超爽视频在线观看| 国产亚洲91精品色在线| 国产精品国产三级专区第一集| 成人特级av手机在线观看| 欧美丝袜亚洲另类| 日韩欧美一区视频在线观看 | 日韩人妻高清精品专区| 青青草视频在线视频观看| 天堂网av新在线| 七月丁香在线播放| 精品久久久久久久久久久久久| 欧美bdsm另类| 九九爱精品视频在线观看| av国产免费在线观看| 美女高潮的动态| 亚洲精品视频女| 麻豆成人午夜福利视频| av网站免费在线观看视频 | 国产黄片美女视频| 亚洲精品久久午夜乱码| 国产一区二区三区综合在线观看 | 人人妻人人澡欧美一区二区| 爱豆传媒免费全集在线观看| 五月天丁香电影| 国产成人午夜福利电影在线观看| 又大又黄又爽视频免费| 国产淫片久久久久久久久| 日日摸夜夜添夜夜添av毛片| 99久久精品热视频| 国产精品久久久久久久久免| 久久国产乱子免费精品| 婷婷色av中文字幕| 久久99蜜桃精品久久| 国产乱来视频区| 午夜福利在线在线| 精品人妻熟女av久视频| 国内少妇人妻偷人精品xxx网站| 99久国产av精品国产电影| 欧美三级亚洲精品| 99久久精品国产国产毛片| 亚洲成人av在线免费| 两个人视频免费观看高清| 免费av观看视频| 少妇的逼好多水| 熟妇人妻不卡中文字幕| 久久精品国产自在天天线| 欧美成人精品欧美一级黄| 亚洲欧美精品专区久久| 成人鲁丝片一二三区免费| 人人妻人人澡欧美一区二区| 又爽又黄无遮挡网站| 国产精品无大码| 又爽又黄无遮挡网站| 黄片无遮挡物在线观看| 亚洲国产成人一精品久久久| 最新中文字幕久久久久| 亚洲精品乱码久久久v下载方式| 黄片wwwwww| 国产单亲对白刺激| 亚洲成人中文字幕在线播放| 欧美 日韩 精品 国产| 深夜a级毛片| 美女高潮的动态| 国产精品无大码| 国产单亲对白刺激| 天天躁夜夜躁狠狠久久av| 麻豆成人午夜福利视频| 亚洲av中文av极速乱| 免费在线观看成人毛片| 久久国产乱子免费精品| 亚洲美女搞黄在线观看| 最近最新中文字幕免费大全7| 亚洲人成网站在线播| av国产免费在线观看| 欧美丝袜亚洲另类| 日本与韩国留学比较| 久久精品国产亚洲网站| 91aial.com中文字幕在线观看| 成人二区视频| 男人舔女人下体高潮全视频| 欧美高清性xxxxhd video| 国产伦精品一区二区三区视频9| 久久久久久久久久久丰满| 国内揄拍国产精品人妻在线| 久久精品国产鲁丝片午夜精品| 亚洲av.av天堂| 丝瓜视频免费看黄片| 国产精品久久久久久精品电影| 老师上课跳d突然被开到最大视频| 亚洲伊人久久精品综合| 午夜久久久久精精品| 亚洲精品色激情综合| 联通29元200g的流量卡| 最近视频中文字幕2019在线8| 亚洲人成网站高清观看| 日韩精品有码人妻一区| 天堂俺去俺来也www色官网 | 婷婷色av中文字幕| 成人毛片60女人毛片免费| 青春草亚洲视频在线观看| 特大巨黑吊av在线直播| 久久久午夜欧美精品| 亚洲国产最新在线播放| 美女被艹到高潮喷水动态| 男人舔女人下体高潮全视频| 一级黄片播放器| 欧美日韩综合久久久久久| 狂野欧美激情性xxxx在线观看| 丝袜喷水一区| 少妇被粗大猛烈的视频| 麻豆乱淫一区二区| 天堂中文最新版在线下载 | 久久综合国产亚洲精品| 少妇高潮的动态图| 国产亚洲精品久久久com| 永久免费av网站大全| 成人性生交大片免费视频hd| 日日啪夜夜撸| 国产精品久久久久久久久免| 99热网站在线观看| 国产欧美日韩精品一区二区| 在线观看美女被高潮喷水网站| 欧美激情久久久久久爽电影| 国产在视频线精品| 22中文网久久字幕| 亚洲一区高清亚洲精品| 亚洲欧美成人综合另类久久久| 中文在线观看免费www的网站| xxx大片免费视频| 80岁老熟妇乱子伦牲交| 在线观看美女被高潮喷水网站| 色综合色国产| 99久国产av精品国产电影| 天天躁夜夜躁狠狠久久av| 麻豆av噜噜一区二区三区| 久久精品久久久久久噜噜老黄| 国产精品一二三区在线看| 久久久久久久久久久免费av| 大香蕉久久网| 国产黄a三级三级三级人| 极品少妇高潮喷水抽搐| 精品久久久久久电影网| 日本三级黄在线观看| 在线观看一区二区三区| 又爽又黄无遮挡网站| 免费观看av网站的网址| 啦啦啦中文免费视频观看日本| 国产伦精品一区二区三区四那| 国产欧美另类精品又又久久亚洲欧美| 久久久精品免费免费高清| 国产精品不卡视频一区二区| 国产精品一及| 女的被弄到高潮叫床怎么办| 插逼视频在线观看| 美女国产视频在线观看| 日韩欧美国产在线观看| 丰满人妻一区二区三区视频av| 午夜久久久久精精品| 国产精品一及| 精品久久久噜噜| 色哟哟·www| 日韩电影二区| 国产精品人妻久久久影院| 国产色爽女视频免费观看| 国产成年人精品一区二区| 国产在线一区二区三区精| 国产永久视频网站| 国模一区二区三区四区视频| 伊人久久精品亚洲午夜| 嫩草影院新地址| 国产成人精品福利久久| 欧美激情在线99| 伊人久久精品亚洲午夜| 欧美zozozo另类| 亚洲经典国产精华液单| 欧美成人一区二区免费高清观看| av.在线天堂| 男人爽女人下面视频在线观看| 免费观看在线日韩| 欧美xxxx黑人xx丫x性爽| 一个人看视频在线观看www免费| 日本猛色少妇xxxxx猛交久久| 大又大粗又爽又黄少妇毛片口| 精品久久久久久久久av| 日韩在线高清观看一区二区三区| 观看美女的网站| 亚洲经典国产精华液单| 国产综合精华液| 午夜免费男女啪啪视频观看| 国产高清国产精品国产三级 | 日韩伦理黄色片| a级毛色黄片| 1000部很黄的大片| 大香蕉97超碰在线| 九九在线视频观看精品| 欧美成人一区二区免费高清观看| 99久久九九国产精品国产免费| 国产黄片视频在线免费观看| 搞女人的毛片| 综合色丁香网| 日韩成人伦理影院| 国产亚洲最大av| 少妇的逼水好多| 综合色av麻豆| 伦精品一区二区三区| 一区二区三区乱码不卡18| 神马国产精品三级电影在线观看| 亚洲av在线观看美女高潮| 国国产精品蜜臀av免费| 国产黄片美女视频| 少妇人妻精品综合一区二区| 久久99热这里只有精品18| 成年女人在线观看亚洲视频 | 欧美日韩亚洲高清精品| 国产一区亚洲一区在线观看| 亚洲在久久综合| 婷婷色综合www| 久久99蜜桃精品久久| 在线观看人妻少妇| 免费大片18禁| av天堂中文字幕网| 国产精品国产三级国产专区5o| 久久99热这里只有精品18| 中文字幕av在线有码专区| 少妇猛男粗大的猛烈进出视频 | 夫妻午夜视频| 亚洲成色77777| 三级毛片av免费| 精品国产三级普通话版| 国产午夜精品一二区理论片| av国产久精品久网站免费入址| 午夜福利在线在线| 国产 一区 欧美 日韩| 欧美性感艳星| 亚洲第一区二区三区不卡| 国产精品伦人一区二区| 国产亚洲91精品色在线| 国产毛片a区久久久久| 国产人妻一区二区三区在| 久久久久精品久久久久真实原创| 成人午夜精彩视频在线观看| 18禁在线无遮挡免费观看视频| 亚洲av国产av综合av卡| 老师上课跳d突然被开到最大视频| 18禁在线播放成人免费| 国产午夜福利久久久久久| 蜜桃亚洲精品一区二区三区| 2018国产大陆天天弄谢| 三级经典国产精品| 久久久久性生活片| 爱豆传媒免费全集在线观看| 天天一区二区日本电影三级| 国产精品久久久久久精品电影小说 | 免费av观看视频| 一本久久精品| 亚洲欧美日韩无卡精品| 联通29元200g的流量卡| av卡一久久| 日产精品乱码卡一卡2卡三| 老女人水多毛片| 国产黄色小视频在线观看| 我的老师免费观看完整版| 亚洲久久久久久中文字幕| 国产视频首页在线观看| 日本免费在线观看一区| 欧美3d第一页| 久久久国产一区二区| 一个人看的www免费观看视频| 在线免费观看不下载黄p国产| 色吧在线观看| 日韩,欧美,国产一区二区三区| 亚洲成人久久爱视频| 久久久久久久久大av| 内射极品少妇av片p| 国产老妇伦熟女老妇高清| 最新中文字幕久久久久| 亚洲精品一二三| 亚洲av免费高清在线观看| 日韩精品青青久久久久久| 久热久热在线精品观看| 99热网站在线观看| 久久99热6这里只有精品| 久久这里有精品视频免费| or卡值多少钱| 成年版毛片免费区| 男人和女人高潮做爰伦理| 国产亚洲5aaaaa淫片| 中文字幕制服av| av又黄又爽大尺度在线免费看| 国产精品不卡视频一区二区| 一区二区三区免费毛片| 中文字幕av成人在线电影| 超碰97精品在线观看| 久久99蜜桃精品久久| 亚洲精品乱码久久久v下载方式| 亚洲国产av新网站| 久久久a久久爽久久v久久| 亚洲欧洲日产国产| 麻豆成人av视频| av卡一久久| 亚洲av日韩在线播放| 日韩一区二区三区影片| 国产一区二区在线观看日韩| 国产色爽女视频免费观看|