农业工程学报
農業工程學報
농업공정학보
2014年
7期
64-71
,共8页
陈冲%胡克林%张玲娥%牛灵安
陳遲%鬍剋林%張玲娥%牛靈安
진충%호극림%장령아%우령안
土壤%模型%碳%县域尺度%冲积平原区%垂向分布模型%空间分布
土壤%模型%碳%縣域呎度%遲積平原區%垂嚮分佈模型%空間分佈
토양%모형%탄%현역척도%충적평원구%수향분포모형%공간분포
soils%models%carbon%county scale%alluvial plain area%vertical distribution model%spatial distribution
冲积平原区通常具有复杂的剖面质地层次排列,为了准确估算冲积平原区土壤碳密度的空间分布特征,该文在华北冲积平原区的河北曲周县选取了121个土壤剖面,测定了各土层有机碳含量,构建了基于负指数函数的土壤有机碳垂向分布模型,结合地统计学方法绘制了该县土壤碳密度的空间分布图。结果表明,土壤有机碳含量随深度增加呈逐渐递减的趋势,各土层有机碳含量均属于中等变异程度。0~20和>20~40 cm土壤有机碳空间连续性较好,它们的空间相关距离分别为14和3 km,而下层(>40 cm)土壤有机碳均表现为纯块金效应结构。土壤有机碳垂向分布模型可以很好地描述剖面土壤有机碳含量的变化特征,且预测与实测的土壤有机碳含量的均方根误差仅为0.70 kg/m3,决定系数达到了0.95。曲周县土壤有机碳密度的空间分布总体表现为西北高东南低的趋势。其空间分布主要受土壤类型和质地的影响,其中潮土和盐化潮土的碳密度明显高于褐土化潮土,质地较细的土壤(轻壤、中壤和粘土)碳密度明显高于质地较粗的土壤(砂土和砂壤)。该研究为冲积平原区土壤碳密度的估算提供了一种新的方法。
遲積平原區通常具有複雜的剖麵質地層次排列,為瞭準確估算遲積平原區土壤碳密度的空間分佈特徵,該文在華北遲積平原區的河北麯週縣選取瞭121箇土壤剖麵,測定瞭各土層有機碳含量,構建瞭基于負指數函數的土壤有機碳垂嚮分佈模型,結閤地統計學方法繪製瞭該縣土壤碳密度的空間分佈圖。結果錶明,土壤有機碳含量隨深度增加呈逐漸遞減的趨勢,各土層有機碳含量均屬于中等變異程度。0~20和>20~40 cm土壤有機碳空間連續性較好,它們的空間相關距離分彆為14和3 km,而下層(>40 cm)土壤有機碳均錶現為純塊金效應結構。土壤有機碳垂嚮分佈模型可以很好地描述剖麵土壤有機碳含量的變化特徵,且預測與實測的土壤有機碳含量的均方根誤差僅為0.70 kg/m3,決定繫數達到瞭0.95。麯週縣土壤有機碳密度的空間分佈總體錶現為西北高東南低的趨勢。其空間分佈主要受土壤類型和質地的影響,其中潮土和鹽化潮土的碳密度明顯高于褐土化潮土,質地較細的土壤(輕壤、中壤和粘土)碳密度明顯高于質地較粗的土壤(砂土和砂壤)。該研究為遲積平原區土壤碳密度的估算提供瞭一種新的方法。
충적평원구통상구유복잡적부면질지층차배렬,위료준학고산충적평원구토양탄밀도적공간분포특정,해문재화북충적평원구적하북곡주현선취료121개토양부면,측정료각토층유궤탄함량,구건료기우부지수함수적토양유궤탄수향분포모형,결합지통계학방법회제료해현토양탄밀도적공간분포도。결과표명,토양유궤탄함량수심도증가정축점체감적추세,각토층유궤탄함량균속우중등변이정도。0~20화>20~40 cm토양유궤탄공간련속성교호,타문적공간상관거리분별위14화3 km,이하층(>40 cm)토양유궤탄균표현위순괴금효응결구。토양유궤탄수향분포모형가이흔호지묘술부면토양유궤탄함량적변화특정,차예측여실측적토양유궤탄함량적균방근오차부위0.70 kg/m3,결정계수체도료0.95。곡주현토양유궤탄밀도적공간분포총체표현위서북고동남저적추세。기공간분포주요수토양류형화질지적영향,기중조토화염화조토적탄밀도명현고우갈토화조토,질지교세적토양(경양、중양화점토)탄밀도명현고우질지교조적토양(사토화사양)。해연구위충적평원구토양탄밀도적고산제공료일충신적방법。
Soil organic carbon (SOC) is the key indicator in assessing soil quality, and it is also the important source and sink in global carbon cycle. Usually, the stratified summation method is used in estimation of SOC concentration at small scale, but it is costly and time-consuming process since it needs a large number of soil samples at regional scale. Recently, the vertical distribution models, such as the negative exponential, power and logarithmic functions are used to describe the changes of SOC content with the increasing of soil depth. The vertical distribution of soil texture in alluvial plain is very complicated. However, there are few reports on assessment of the suitability of the SOC vertical distribution model in an alluvial plain. The objectives of this study were to construct and assess a vertical distribution model to describe the changes of SOC content in an alluvial plain, and to determine the main variables that affected SOC concentration distribution. In this study, 605 soil samples were collected from 121 soil profiles in an alluvial plain area of Quzhou county, Hebei Province. SOC contents from topsoil to 1-m depth were determined. The vertical distribution model of SOC was constructed based on negative exponential function, and then regional spatial distribution of SOC concentration was obtained by geostatistical methods. The results indicated that SOC content showed a gradually decreasing trend with the increase of soil depth, and the mean SOC content in topsoil was the highest, reached to 8.25 g/kg soil. The coefficients of variation of SOC content for all layers ranged from 0.26 to 0.43, and all belonged to moderate degree of variation. The spatial continuity was better for SOC in 0-20 and>20-40 cm as compared to the rest soil depths, and their correlation distances were 14 and 3 km, respectively. However, SOC in subsoil (>40 cm) showed a pure nugget effect, which reflected the complex spatial distribution of soil textural layers in an alluvial plain. The negative exponential model can well describe the changes of SOC content with the increasing of depth in alluvial plain area, the root mean squared error was only 0.70 and the coefficient of determination of the predicted and measured SOC contents reached to 0.95. Spatial distribution of SOC density showed a decreasing trend from northwest to southeast across the county. Soil types and soil texture were the main influencing factors. The SOC concentration of fluvo-aquic soil and salinity fluvo-aquic soil were significantly higher than that of cinnamon fluvo-aquic soil. The SOC concentration of fine textural soil (light loam, medium loam and clay) was significantly higher than that of the coarse textural soil (sand and sandy loam). The constructed vertical distribution model can well describe the changes of SOC content in soil profile, which not only provides a new method to estimate SOC contentin alluvial plain area, but also can serve as guidance on evaluation and improvement of regional soil fertility.