桂西北喀斯特坡地土壤137Cs的剖面分布特征及其指示意义

分析了¹³⁷Cs及土壤有机碳（SOC）在桂西北典型峰丛坡地及岩溶裂隙中的剖面分布特征,探讨了¹³⁷Cs方法在喀斯特坡地的适用性及其指示的坡面土壤侵蚀特征.结果表明：所有剖面¹³⁷Cs与SOC均显著相关,两者可能有相同的流失途径;次生林坡地¹³⁷Cs主体分布深度在24 cm以内,中上及中坡剖面随深度呈指数递减分布,地表无侵蚀或侵蚀轻微,坡脚剖面呈较严重侵蚀形态;坡耕地剖面¹³⁷Cs在耕层内均匀分布,中上坡及中坡主体分布深度在15 cm左右,面积活度远低于背景值,土壤侵蚀剧烈,坡脚分布深度至45 cm,呈堆积形态;次生林坡脚剖面、耕地中上坡剖面及所有裂隙剖面,¹³⁷Cs在主体分布深度以下有断续极微量的分布,指示了喀斯特坡地土壤颗粒有随降雨沿地表负地形向地下流失的趋势,但流失量轻微.     

137Cs和210Pbex示踪黑土区坡耕地土壤侵蚀对有机碳的影响

通过在野外28.5 hm2的坡耕地上采集土壤样品,定量评价了利用137Cs和210Pbex研究土壤有机碳(SOC)动态的潜力,以探讨东北黑土区土壤侵蚀对土壤有机碳的影响.结果表明:农耕地土壤137Cs、210Pbex和SOC在平面和垂直深度上均具有相似的分布特征.在平面上,尽管受土壤侵蚀沉积的影响,137Cs、210Pbex面积活度及SOC储量变异很大,但它们具有相同的变化趋势.在垂直断面上,侵蚀区137Cs、210Pbex和SOC在0～25 cm耕层内分布均匀,25 cm以下放射性活度减小,SOC含量也相应下降;沉积区0～100 cm深度上137Cs和210Pbex呈现先增加后减小的分布规律,SOC也具有类似的变化特征.农耕地SOC与137Cs、210Pbex呈显著线性相关,表明它们在黑土区农耕地上具有相似的物理运移特征,137Cs和210Pbex可直接用来定量评价黑土侵蚀下SOC的时空分布特点.     

利用137Cs技术研究黑土坡耕地土壤再分布特征

利用¹³⁷Cs示踪技术和不同的理论模型研究典型的东北漫岗地形的黑土土壤再分布状况.通过野外采样和模型分析,得出研究区¹³⁷Cs背景值为2 232.75 Bq·m^-2,介于长江三角洲和黄土高原背景值之间,表明¹³⁷Cs沉降与纬度和降水相关.研究区各地貌部位¹³⁷Cs含量在水平方向和深度分布上有很大的分异.坡肩部位¹³⁷Cs含量最低,土壤侵蚀最为强烈;坡顶和坡背侵蚀较为微弱;坡脚和坡足基本上表现土壤沉积.¹³⁷Cs分布深度从坡肩20 cm到坡足80 cm土层,表现出该区经历了强烈的侵蚀和沉积过程.文中采用4种常用的¹³⁷Cs土壤侵蚀模型估计研究区的土壤侵蚀速率,结果表明,PM模型明显低估了土壤侵蚀速率,MBM-1明显高估了土壤侵蚀速率,MBM-2和MBM-3估计的结果较为相近的合理结果.     

喀斯特坡地基岩起伏对土壤剖面水分格局的影响

研究了喀斯特地区典型坡地3条人工开挖样沟(投影长21 m、宽1 m)的岩土结构特征、土壤剖面平均含水量和土岩界面含水量沿坡面向下的变化趋势,探讨了喀斯特坡地基岩起伏对土壤水分格局的影响.结果表明: 喀斯特坡地地表地形与基岩地形不一致,基岩深度变异系数最大为82%,基岩起伏较大.基岩起伏程度明显影响到土壤剖面水分分布格局: 基岩起伏较小时,土壤含水量呈上坡位至下坡位逐渐增加的趋势,且土壤剖面平均含水量和土岩界面含水量与基岩深度相关性均不显著;基岩起伏越大,土壤含水量沿坡向下线性增加的趋势越不明显,土壤水分空间连续性越差,基岩凹陷、裂隙处土壤含水量较高,土壤剖面平均含水量和土岩界面含水量与基岩深度呈极显著正相关,但后者对基岩起伏的响应更明显.     

坡耕地紫色土养分空间变异对土壤侵蚀的响应

坡耕地土壤侵蚀导致土壤质量降低,并因此造成对作物产量的不利影响。利用土壤侵蚀测定的^137Cs示踪技术,结合土壤理化分析,研究了川中丘陵区紫色土坡耕地土壤侵蚀所引起的土壤再分配对养分空间变异性的影响。结果表明,川中丘陵区坡耕地土壤侵蚀是水蚀和耕作侵蚀共同作用的结果,强烈的耕作导致坡上部发生最为严重的土壤侵蚀。土壤侵蚀对土壤特性的空间变异性产生深刻影响,坡上部土壤有机质和养分贫瘠,而在坡下部相对富集;土壤有机质、全N、碱解N、有效P、K以及土壤粘粒含量在不同坡位之间出现显著差异。反映净余土壤再分配速率的^137Cs面积浓度与这些土壤理化特性均有密切的相关性。因此,^137Cs面积浓度可以作为表征侵蚀坡地土壤综合质量的指标。     

137Cs和210Pbex示踪黑土区坡耕地

通过在野外28.5 hm²的坡耕地上采集土壤样品,定量评价了利用¹³⁷Cs和²¹⁰Pb_ex研究土壤有机碳(SOC)动态的潜力,以探讨东北黑土区土壤侵蚀对土壤有机碳的影响.结果表明:农耕地土壤¹³⁷Cs、²¹⁰Pb_ex和SOC在平面和垂直深度上均具有相似的分布特征.在平面上,尽管受土壤侵蚀沉积的影响,¹³⁷Cs、²¹⁰Pb_ex面积活度及SOC储量变异很大,但它们具有相同的变化趋势.在垂直断面上,侵蚀区¹³⁷Cs、²¹⁰Pb_ex和SOC在0～25 cm耕层内分布均匀,25 cm以下放射性活度减小,SOC含量也相应下降;沉积区0～100 cm深度上¹³⁷Cs和²¹⁰Pb_ex呈现先增加后减小的分布规律,SOC也具有类似的变化特征.农耕地SOC与¹³⁷Cs、²¹⁰Pb_ex呈显著线性相关,表明它们在黑土区农耕地上具有相似的物理运移特征,¹³⁷Cs和²¹⁰Pb_ex可直接用来定量评价黑土侵蚀下SOC的时空分布特点.     

红壤侵蚀区植被恢复过程中土壤种子库变化特征

土壤侵蚀作为一种自然营力和自然干扰形式对土壤种子库的次分布与物种组成具有一定的影响。本研究对典型红壤侵蚀区裸地(Ⅰ号)、马尾松林地(Ⅱ、Ⅲ、Ⅳ号)和次生林(Ⅴ号)等5处不同植被恢复区的土壤种子库物种组成、储量及分布格局进行研究,探究在植被恢复过程中土壤侵蚀对土壤种子库的影响。结果表明: 研究区土壤种子库共统计到21种物种,物种丰富度低,以草本种类为主。各样地土壤种子库密度为56.7～793.3粒·m^-2,样地间差异显著,土壤种子库密度随着土壤侵蚀强度加重而明显下降。各样地浅层0～2 cm土壤种子库密度随着上坡-中坡-下坡的变化均呈增加趋势;剧烈侵蚀地和强烈侵蚀地土壤种子库主要分布在5～10 cm深层土壤内,且中上坡0～2 cm土层几乎没有种子。土壤侵蚀使得土壤种子库在土层中的分布呈现深层化,植被恢复后深层种子库积累仍需要较长的时间。     

黑土坡耕地有机碳及其组分累积-损耗格局对耕作侵蚀与水蚀的响应

耕作与水蚀是黑土区坡耕地碳库退化的主导因素,为进一步探究土壤有机碳(SOC)及其组分对不同侵蚀驱动力(耕作、水力)的响应格局,基于该区耕作侵蚀与水蚀模型,在定量表达耕作侵蚀-沉积量与水蚀量的基础上,利用地统计学的方法,分析了东北黑土区典型漫岗地形坡面尺度SOC及其3种组分的空间分布特征.结果表明: 耕作侵蚀与沉积速率分别表现为坡上>坡下>坡中>坡脚和坡脚>坡下>坡中>坡上;水蚀速率表现为坡下>坡脚>坡中>坡上;坡下陡坡位置耕作侵蚀与水蚀协同引起严重的土壤流失.虽然耕作侵蚀速率(0.02～7.02 t·hm^-2·a^-1)远小于水蚀速率(5.96～101.17 t·hm^-2·a^-1),但耕作侵蚀在全坡面范围均可对SOC产生不同程度的影响,而水蚀则主要在坡下径流汇集区显著影响SOC的累积-损耗.受水蚀与耕作侵蚀-沉积作用影响,SOC、颗粒有机碳、水溶性有机碳在侵蚀点含量低于沉积点,而微生物生物量碳变化趋势相反;耕作侵蚀通过影响颗粒有机碳参与SOC的积累-损耗过程.     

137Cs示踪技术研究坡耕地黑土侵蚀和沉积特征

准确地测定研究区137Cs背景值,建立137Cs流失量与土壤再分布速率之间的定量模型是137Cs示踪技术的关键。通过野外选择参照样地和利用热核爆炸源137Cs背景值模型来确定研究区137Cs的背景值,在此基础上用体现耕作迁移的质量平衡模型估算黑土坡耕地不同地貌部位的土壤再分布速率,并对主要参数进行敏感性分析。结果表明(1)研究区实测的137Cs背景值为2376.81±108.46Bq/m2,模型预测值为2318.4Bq/m2,模型预测远离西北核试验基地的地区较为准确。(2)研究区中坡位(坡肩和坡背)137Cs含量最低,侵蚀最为强烈,平均侵蚀速率为33.56t/(hm2·a)和21.67t/(hm2·a);坡麓和坡足则明显表现沉积,平均沉积速率为-4.93t/(hm2·a)和-24.61t/(hm2·a)。(3)模型预测的侵蚀速率与耕层质量深度(d)、张驰深度(H)正相关,而与137Cs年沉降易被迁移的比例(γ)和颗粒校正因子(P)反相关。并且,模型对参数d、p的敏感性分别高于参数H和γ。     

红壤坡地不同土地利用方式土壤侵蚀的时空分布规律研究

应用定位土芯Eu(Europium)示踪新方法 ,研究红壤坡地不同土地利用方式下土壤侵蚀的时空分布规律 .结果表明 ,新方法对以片蚀和细沟侵蚀为主的红壤坡地是适用的 ;土壤侵蚀的时间分布与降雨量的年时间分布相一致 ,过程性暴雨期表现为全年土壤侵蚀的高峰期 ;在复合坡面 ,随坡面的陡、缓、凹 ,土壤侵蚀表现强、弱、沉积 ;相同坡度和坡长条件下 ,幼龄板栗园的土壤侵蚀速率 >雷竹园 >稀疏马尾松林地 >茶园 .     

Stocks and dynamics of SOC in relation to soil redistribution by water and tillage erosion

Soil organic carbon (SOC) displaced by soil erosion is the subject of much current research and the fundamental question, whether accelerated soil erosion is a source or sink of atmospheric CO₂, remains unresolved. A toposequence of terraced fields as well as a long slope was selected from hilly areas of the Sichuan Basin, China to determine effects of soil redistribution rates and processes on SOC stocks and dynamics. Soil samples for the determination of caesium‐137 (¹³⁷Cs), SOC, total N and soil particle size fractions were collected at 5 m intervals along a transect down the two toposequences. ¹³⁷Cs data showed that along the long slope transect soil erosion occurred in upper and middle slope positions and soil deposition appeared in the lower part of the slope. Along the terraced transect, soil was lost over the upper parts of the slopes and deposition occurred towards the downslope boundary on each terrace, resulting in very abrupt changes in soil redistribution over short distances either side of terrace boundaries that run parallel with the contour on the steep slopes. These data reflect a difference in erosion process; along the long slope transect, water erosion is the dominant process, while in the terraced landscape soil distribution is mainly the result of tillage erosion. SOC inventories (mass per unit area) show a similar pattern to the ¹³⁷Cs inventory, with relatively low SOC content in the erosional sites and high SOC content in depositional areas. However, in the terraced field landscape C/N ratios were highest in the depositional areas, while along the long slope transect, C/N ratios were highest in the erosional areas. When the samples are subdivided based on ¹³⁷Cs‐derived erosion and deposition data, it is found that the erosional areas have similar C/N ratios for both toposequences, while the C/N ratios in depositional areas are significantly different from each other. These differences are attributed to the difference in soil erosion processes; tillage erosion is mainly responsible for high‐SOC inventories at depositional positions on terraced fields, whereas water erosion plays a primary role in SOC storage at depositional positions on the long slope. These data support the theory that water erosion may cause a loss of SOC due to selective removal of the most labile fraction of SOC, while on the other hand tillage erosion only transports the soil over short distances with less effect on the total SOC stock.     

Horizontal migration of 137Cs with water erosion of soils

The results of research of horizontal migration of 137Cs with soils water erosion are presented. It was found that quantitative parameters of 137Cs migration depended on radioactive pollution of cultivated soil layer, volume of water erosion of soils and character of usage of sloping lands. Activity of 137Cs in lower parts of slopes was 37-295 kBq/m2 higher than in the middle and apex parts of slopes. Increase in 137Cs activity varied from 10 to 18 percent in accumulation zone as compared to outwash zone with soil losses 5.0 t/ha and from 17 to 35 percent with soil losses 5.1-10.0 t/ha and from 30 to 127 percent with soil losses 10. 1-20.0 t/ha.     

The dynamics of soil redistribution and the implications for soil organic carbon accounting in agricultural south‐eastern Australia

Anthropogenically induced change in soil redistribution plays an important role in the soil organic carbon (SOC) budget. Uncertainty of its impact is large because of the dearth of recent soil redistribution estimates concomitant with changing land use and management practices. An Australian national survey used the artificial radionuclide caesium‐137 (¹³⁷Cs) to estimate net (1950s–1990) soil redistribution. South‐eastern Australia showed a median net soil loss of 9.7 t ha^?1 yr^?1. We resurveyed the region using the same ¹³⁷Cs technique and found a median net (1990–2010) soil gain of 3.9 t ha^?1 yr^?1 with an interquartile range from ?1.6 t ha^?1 yr^?1 to +10.7 t ha^?1 yr^?1. Despite this variation, soil erosion across the region has declined as a likely consequence of the widespread adoption of soil conservation measures over the last ca 30 years. The implication of omitted soil redistribution dynamics in SOC accounting is to increase uncertainty and diminish its accuracy.     

Response of changes in soil nutrients to soil erosion on a purple soil of cultivated sloping land

Severe soil erosion of cultivated sloping land in hilly areas of Sichuan, China, has resulted in deterioration of soil quality, and therefore has an adverse impact on crop production. A hillslope of 110 m in length was selected with a slope steepness of 10.12% where the soils were classified as Regosols. Soil samples for determining ¹³⁷Cs, soil organic matter (SOM), total N, P, K, available N, P, K and particle size fraction were collected at 10 m intervals along a transect of the hillslope. Loss of soil nutrients owing to soil erosion was studied by using ¹³⁷Cs technique, and the relationships between ¹³⁷Cs-derived soil redistribution rates and soil nutrients were established over the cultivated sloping land in hilly areas of Sichuan, China (30o26′N, 104o28′E). The values of SOM, total N, available N, P, K and the soil particle fractions of size < 0.002 mm were smaller at upper and middle slope positions where ¹³⁷Cs inventories were lower (i.e., soil erosion rates were higher) than at downslope positions where ¹³⁷Cs inventories were higher (i.e., soil erosion rates were lower). The lowest ¹³⁷Cs inventories were found at the hilltop, showing that besides erosion owing to water flow, tillage also contributed to soil losses, and intensive tillage was mostly responsible for severe erosion at upper slope positions. There were significant differences in SOM, total N, available N, P, K and the soil particle fractions of size < 0.002 mm between different slope segments, and these properties were significantly correlated with slope length. These soil properties were also significantly correlated with ¹³⁷Cs inventories, indicating that both ¹³⁷Cs and nutrient concentrations varied with topographical changes. The variation in soil properties was strongly influenced by erosion-induced soil redistribution, and therefore ¹³⁷Cs inventories mirroring soil redistribution rates would be considered as an integrated indicator of soil quality.     

桂西北喀斯特洼地土壤有机碳和速效磷的空间变异

空间变异性的研究有助于认识土壤养分的空间分布特征与生态过程之间的关系。采用网格取样(20m×20m),利用地统计学方法分析了典型喀斯特洼地土壤有机碳(SOC)和速效磷(AP)的空间变异特征。结果表明SOC和AP的半变异函数分别用球状模型和指数模型拟合的效果较好。块金效应对SOC和AP总变异的贡献分别为37.9%和49.8%,说明SOC主要受结构性因素控制,而AP受结构性因素和随机因素双重控制。SOC的分布呈明显的带状各向异性特征,在洼地的长轴方向具有较大的变程和较小的基台值,其全向半变异函数的相关距离为135.5m,与洼地不同种植类型地块的覆盖尺度基本相当。AP的分布特征与SOC存在明显差异,具有较大的漂移趋势,其相关距离为413.4m;但在分离漂移趋势后,其相关距离为167.4m,反映了不同地块间的施肥差异对AP的影响较大。喀斯特洼地SOC的空间分布主要受地形和土地利用结构控制,而AP的分布的规律性不明显,可能与施肥等因素的随机性较强有关。     

喀斯特地区坡耕地与退耕地土壤有机碳空间异质性及其影响因素

利用网格采样(10 m×10 m),对比分析了典型喀斯特坡耕地(长期耕作)和退耕地(自然恢复)表层(0—15 cm)土壤有机碳(SOC)的空间变异特征,以期探究退耕恢复20a后SOC的空间异质性及其主要影响因素的变化。结果表明退耕地SOC含量(75.5 g/kg)显著高于坡耕地(15.1 g/kg),为坡耕地的5.0倍,说明自然恢复能显著提高SOC累积量;半变异函数分析结果表明退耕地基台值(521.7)为坡耕地(25.7)的14.9倍,说明退耕地SOC空间异质性远大于坡耕地。坡耕地和退耕地SOC的主要影响因子存在较大差异,土地覆盖类型、坡位、岩石出露率以及三者的交互作用显著控制着坡耕地SOC的空间格局,其贡献率分别为9.1%、6.3%、4.6%以及17.0%;土壤水分、坡度、岩石出露率以及三者的交互作用显著控制退耕地SOC的空间格局,其贡献率分别为26.0%、10.7%、7.2%以及3.6%;尽管岩石出露率对坡耕地和退耕地SOC的空间格局均有显著影响,但坡耕地SOC的主要控制因子为土地覆盖类型以及各因子的交互作用,而退耕地的主要控制因子为土壤水分。以上研究表明随着植被恢复和物种多样性增加,喀斯特坡地SOC的累积量和空间异质性增强,自然因素对SOC空间格局影响凸显,而岩石出露率始终控制SOC空间格局。     

喀斯特山区不同植被类型土壤有机碳的变化

研究了贵州西南部典型喀斯特山区不同植被类型下常规土壤及小生境土壤中有机碳及不同粒径土壤颗粒有机碳的变化.结果表明:不同植被类型下,常规及小生境土壤有机碳含量均表现为:裸地＜草丛＜灌木林＜乔木林,常规土壤变幅在7.18 ～43.42 g·kg-1,土面和石坑土壤有机碳变幅分别为6.62 ～46.47 g· kg-1和9.01 ～52.07 g·kg-1;颗粒有机碳(POC)/矿物结合态有机碳( MOC)值均为:裸地＜草丛＜乔木林＜灌木林,同一植被类型下,与常规及土面相比,石坑中土壤POC/MOC值最高;植被在由裸地-草丛-灌木林-乔木林的变化过程中,不同粒径土壤颗粒有机碳含量增加,而土壤有机碳主要以砂粒及粉砂粒有机碳形式存在,说明喀斯特地区土壤的固碳能力及有机碳稳定性较弱,土壤易受外界干扰而引发有机碳流失,土壤质量存在下降或退化的风险.     

青海湖流域季节性冻土区坡面土壤有机碳分布特征及其影响因素

以高寒半干旱区青海湖流域季节性冻土为研究对象,通过调查采样和室内分析,研究了坡向和坡位对不同深度土壤有机碳含量分布的影响。结果表明：阴、阳坡有机碳含量均随土壤深度增加而下降,但阳坡下降的幅度（64%）明显高于阴坡（44%）。阴坡土壤有机碳平均含量为81.99 g/kg,大于阳坡（61.84 g/kg）;不同坡位,土壤有机碳分布特征因坡向而异,其中阴坡土壤有机碳平均含量表现为坡下（89.60 g/kg）＞坡中（86.52 g/kg）＞坡上（69.87 g/kg）,而阳坡土壤有机碳平均含量表现为坡上（65.71 g/kg）＞坡下（61.42 g/kg）＞坡中（58.39 g/kg）。此外,坡位对不同深度土壤有机碳的影响程度在不同坡向也存在差异。阴坡坡位因子对深层土壤有机碳影响显著,而阳坡坡位因子对浅层土壤有机碳影响显著。一般线性模型结果表明,坡面土壤有机碳含量主要受土层和坡向的影响,可解释74.52%的变异性。