侵蚀程度对红壤团聚体分布及养分含量的影响

[目的]探讨不同侵蚀程度下红壤团聚体和养分的变化规律,为侵蚀红壤的肥力提升和合理开发利用提供理论依据。[方法]将红壤表层按照不同深度剥离来模拟不同土壤侵蚀程度,比较分析不同侵蚀程度下团聚体稳定性、有机质和各养分的变化规律及其相互关系。[结果]各侵蚀程度红壤团聚体干筛粒级分布规律大体相似,以≥2mm粒级团聚体为优势粒级,与无明显侵蚀土壤相比,强烈侵蚀土壤≥2mm水稳性团聚体含量降低近1/3;随着土壤侵蚀程度增加,土壤碳、氮、磷等养分含量均表现出逐渐减少的规律,其中强烈侵蚀土壤有机质、全氮和全磷含量减少了30%左右,碱解氮含量减少了近50%,速效磷含量减少了80%以上。相关分析表明,土壤有机质、全氮、全磷、碱解氮含量均与≥2 mm团聚体含量、WSA,MWD和GMD值具有较好的正相关性(p0.05),与D和PAD值呈负相关。[结论]不同侵蚀程度对红壤团聚体分布及养分含量有一定影响,可通过增加有机肥来改善侵蚀红壤结构,提高土壤肥力。     

带状套作复光后不同大豆品种干物质积累模型与特征分析

为了研究套作下高产类型大豆复光后的干物质积累特征,本研究共采用14个高、中、低产量水平的大豆为材料,比较了不同大豆产量类型品种与玉米套作,复光后的干物质积累特征差异。结果表明:1)高产类型大豆复光后干物质积累量为32.99 g·plant?1,较中、低产类型分别高26.82%和91.51%(两年均值)。2)不同产量类型大豆复光后干物质积累速率均呈先增加后下降的趋势,复光后最大干物质积累速率和平均干物质积累速率呈高产类型中产类型低产类型,高产类型大豆最大干物重积累速率的时间大致在复光后41~42 d,中低产类型则在复光后33~37 d;高产类型大豆复光后干物质渐增期天数、积累速率和干物质积累量以及快增期和缓增期的积累速率和积累量均显著高于中、低产类型。3)产量与最大干物质积累速率、最大干物质积累速率时间、平均干物质积累速率、渐增期的持续时间及干物质增量、快增期平均积累速率及干物质增量、缓增期平均积累速率及干物质增量呈显著正相关。本研究表明,套作下高产类型大豆复光后较强的干物质积累优势主要表现在复光后渐增期,而复光后渐增期较强的干物质积累能力主要在于其较长的渐增期持续天数。     

基于物元评判模型的土地整理综合效益评价方法研究

利用物元分析理论,将土地整理综合效益的等级、评价指标及其特征值作为物元,确定土地整理综合效益的经典域、节域及待判物元,应用物元和可拓集合中的关联函数建立了土地整理综合效益物元评判模型。并以山西省阳高县王官屯等二乡(镇)土地开发整理项目为例,对土地整理综合效益物元评判模型进行了实证研究,其综合效益的等级属于程度Km(P)=(-0.101,0.037,-0.431),属于"一般"等级,与模糊综合评价结果相似,符合项目区的实际情况。物元模型应用于土地整理综合效益评价作为一种初步的尝试与探索,为定量评价土地整理综合效益提供了一种新的思路。     

Transitioning from standard to minimum tillage: Trade-offs between soil organic matter stabilization, nitrous oxide emissions, and N availability in irrigated cropping systems

Few studies address nutrient cycling during the transition period (e.g., 1–4 years following conversion) from standard to some form of conservation tillage. This study compares the influence of minimum versus standard tillage on changes in soil nitrogen (N) stabilization, nitrous oxide (N₂O) emissions, short-term N cycling, and crop N use efficiency 1 year after tillage conversion in conventional (i.e., synthetic fertilizer-N only), low-input (i.e., alternating annual synthetic fertilizer- and cover crop-N), and organic (i.e., manure- and cover crop-N) irrigated, maize–tomato systems in California. To understand the mechanisms governing N cycling in these systems, we traced ¹⁵N-labeled fertilizer/cover crop into the maize grain, whole soil, and three soil fractions: macroaggregates (>250 μm), microaggregates (53–250 μm) and silt-and-clay (<53 μm). We found a cropping system effect on soil N_new (i.e., N derived from ¹⁵N-fertilizer or -¹⁵N-cover crop), with 173 kg N_new ha⁻¹ in the conventional system compared to 71.6 and 69.2 kg N_new ha⁻¹ in the low-input and organic systems, respectively. In the conventional system, more N_new was found in the microaggregate and silt-and-clay fractions, whereas, the N_new of the organic and low-input systems resided mainly in the macroaggregates. Even though no effect of tillage was found on soil aggregation, the minimum tillage systems showed greater soil fraction-N_new than the standard tillage systems, suggesting greater potential for N stabilization under minimum tillage. Grain-N_new was also higher in the minimum versus standard tillage systems. Nevertheless, minimum tillage led to the greatest N₂O emissions (39.5 g N₂O–N ha⁻¹ day⁻¹) from the conventional cropping system, where N turnover was already the fastest among the cropping systems. In contrast, minimum tillage combined with the low-input system (which received the least N ha⁻¹) produced intermediate N₂O emissions, soil N stabilization, and crop N use efficiency. Although total soil N did not change after 1 year of conversion from standard to minimum tillage, our use of stable isotopes permitted the early detection of interactive effects between tillage regimes and cropping systems that determine the trade-offs among N stabilization, N₂O emissions, and N availability.     

Starving the soil of plant inputs for 50 years reduces abundance but not diversity of soil bacterial communities

If soil communities rely on plant-derived carbon, is biodiversity lost when this primary source is removed? Soil microbial and mesofaunal communities at the Rothamsted Highfield site were compared under a mixed grass sward, arable rotation and a section maintained as a bare-fallow for the past 50 years by regular tillage. Organic matter reserves have been degraded and microbial and mesofaunal numbers and mite diversity have declined in this unique bare-fallow site, where fresh carbon inputs have been drastically reduced. However, it supports a species-rich metabolically active bacterial community of similar diversity to that in soil maintained as grass sward. Thus in contrast to soil mesofauna, bacterial diversity (but not abundance) is apparently independent of plant inputs.     

青藏高原高寒草甸土壤有机质、全氮和全磷含量对不同土地利用格局的响应

草地土地利用格局的变化强烈影响着其土壤营养元素的含量与垂直分布。对青藏高原东北隅高寒草甸不同土地利用格局（封育植被、放牧利用和人工种植）下不同深度（0—10cm、10—20cm和20—40cm）的土壤有机质、全氮和全磷含量的对比研究表明：封育植被下土壤营养元素在表层和深层之间有显著差异（P〈0．05）,与土壤深度表现出一定的负线性相关（R2〉0．40,P〈0．05）。放牧利用和人工种植对营养元素在不同土壤层次的分布无显著影响（P均值〉0．05）,前者的有机质和全氮含量与土壤深度略呈负线性,后者则无此关系。放牧利用和人工种植较显著地（P均值〈0．05）降低了土壤表层有机质和全氮的含量,但增加了土壤表层全磷的含量,对土壤深层的影响较小。人工种植对营养元素含量的影响效果略大于放牧利用,但两者差异不显著。     

Dynamic of organic matter in the heavy fraction after abandonment of cultivated wetlands

The abandonment of cultivated wetland soil increased the contents of light fraction organic matter (LFOM), heavy fraction organic matter (HFOM) and soil organic matter (SOM). The LFOM and HFOM content increased to 13.3 g kg⁻¹ and 62.4 g kg⁻¹ after 5 years whereas they were 8.4 and 47.9 g kg⁻¹ after 9 years of cropping, respectively. Fourteen years after abandonment, HFOM content increased to 104.3 g kg⁻¹. LFOM was positively correlated with HFOM (p < 0.001). A Langmuir equation was used to calculate the highest HFOM value. The value for the natural wetland soil was closed to this theoretical value (140.8 g kg⁻¹). After 14 years of abandonment, the HFOM maximum (HFOM_Max) value was lower than the equilibrium value suggesting that a further increase in HFOM can occur after abandonment. Assuming a linear accumulation (3.87 Mg C ha⁻¹yr⁻¹), it would take approximately 24 years after the abandonment to reach the HFOM_Max value.     

氮肥运筹、配施有机肥和坐水种对春玉米产量与养分吸收转运的影响

采用田间试验方法,研究了氮肥运筹、配施有机肥和坐水种对春玉米产量与养分吸收转运的影响。结果表明,适宜氮肥运筹方式、配施有机肥和坐水种均能显著增加春玉米产量,氮肥两次追肥处理的产量较一次追肥处理的产量增加10.6%～17.0%,配施有机肥增产10.3%～18.0%,坐水种增产9.1%,配施有机肥并坐水种增产20.4%。氮肥两次追施、配施有机肥及配施有机肥并坐水种均能显著提高春玉米干物质最大积累速率和积累总量,分别提高干物质最大积累速率11.1%～29.5%、28.0%～28.8%和32.1%,依次提高干物质积累总量11.9%～15.5%、21.2%～24.4%和26.9%。氮肥两次追施、配施有机肥和坐水种均可提高N、P、K养分最大吸收速率和吸收总量,养分最大吸收速率以K最高,N居中,P最低;养分吸收总量以N最高,K居中,P最低;养分最大吸收速率出现的时间以K最早（57.2～60.4 d）,N居中（65.3～68.5 d）,P最晚（71.4～74.8 d）,三者均早于干物质积累最大速率出现的时间（82.5～89.3 d）。氮肥两次追施、配施有机肥和坐水种均有利于N、P、K养分由营养体向籽粒的转运量、转运效率、籽粒中养分含量以及氮肥利用率的提高,养分转运效率以P最高（59.3%～66.1%）,其次是N（41.5%～55.1%）,K最低（35.9%～38.0%）。在本实验条件下,施氮量为225 kg/hm2,基肥:拔节肥比1:3,配施有机肥结合坐水种,为最佳施肥处理。     

DEM栅格分辨率对多元线性土壤—景观模型及其制图应用的影响

以亚热带丘陵地区为对象,以该区4 km×3 km的5 m、10 m、15 m、20 m、25 m、30 m数字高程模型(DEM)为基础,建立多元线性土壤景观模型,并应用该模型预测研究区内土壤表层有机质含量分布,进而比较不同分辨率DEM中土壤景观模型及其预测制图的精度。结果表明:在本研究区11 km2范围内,随着DEM栅格分辨率降低,坡度、曲率、比汇水面积(对数)频度均表现出了向其中值区集中的趋势;地形因子的这一变化规律对土壤景观模型的影响较小,例如模型的变量、变量系数及R2在不同分辨率DEM中的差异很小;但地形因子的这一变化规律对模型预测制图的精度具有较大影响,各项指标均说明,模型在10~25 m DEM中的制图精度较高,而在更高分辨率(5 m)或更低分辨率(30 m)DEM中较低。本研究结果对其他亚热带丘陵地区具有一定的指示意义。     

黑土区田块尺度土壤有机质含量遥感反演模型

为了对田块尺度土壤有机质进行空间反演并提高模型精度和稳定性,该文以黑龙江省黑土带41.3 hm~2田块为例,获取2016年5月中下旬两期(受限于拍摄周期和天气原因而选择不同卫星影像,2016年5月17日Landsat 8影像和5月25日Sentinel-2A影像)裸土时期遥感影像和4 m分辨率DEM数据;分析单期影像与土壤有机质(soil organic matter,SOM)的关系,两期影像所包含的土壤含水量变化信息与地形因素对SOM预测模型精度的影响,建立基于BP神经网络的SOM遥感反演模型。结果表明:该田块内SOM含量差异较大;利用单期影像预测SOM时,基于红波段和785~899 nm波段建立的预测模型精度(建模均方根误差RMSE 1.033,检验RMSE 1.079)和稳定性(建模决定系数R2 0.677,检验R20.644)较高;两期影像时,基于红波段和1 570~1 650 nm波段建立的预测模型精度(建模RMSE 0.855,检验RMSE 0.898)和稳定性(建模R2 0.792,检验R2 0.797)显著提高;在两期影像模型基础上,加入地形因子作为输入量,模型精度(建模RMSE 0.492,检验RMSE 0.499)和稳定性(建模R2 0.917,检验R2 0.928)进一步提高。研究成果可为土壤碳库估算和农田精准施肥提供理论与技术支持。