Soil reconstruction after mining fails to restore soil function in an Australian arid woodland

The biogeochemical properties of soils drive ecosystem function and vegetation dynamics, and hence soil restoration after mining should aim to reinstate the soil properties and hydrological dynamics of remnant ecosystems. The aim of this study is to assess soil structure in two vegetation types in an arid ecosystem, and to understand how these soil properties compare to a reconstructed soil profile after mining. In an arid ecosystem in southeast Australia, soil samples were collected at five depths (to 105 cm) from remnant woodland and shrubland sites, and sites either disturbed or totally reconstructed after mining. We assessed soil physico‐chemical properties and microbial activity. Soils in the remnant arid ecosystem had coarse‐textured topsoils that overlay clay horizons, which allows water to infiltrate and avoid evaporation, but also slows drainage to deeper horizons. Conversely, reconstructed soils had high sand content at subsoil horizons and high bulk density and compaction at surface layers (0–20 cm). Reconstructed soils had topsoils with higher pH and electrical conductivity. The reconstructed soils did not show increased microbial activity with time since restoration. Overall, the reconstructed soil horizons were not organized in a way that allowed rainfall infiltration and water storage, as is imperative to arid‐zone ecosystem function. Future restoration efforts in arid ecosystems should focus on increasing sand content of soils near the surface, to reduce evaporative water loss and improve soil quality and plant health.     

Advanced mine restoration protocols facilitate early recovery of soil microbial biomass,activity and functional diversity

Many ecosystem restoration programmes can take over 15 years to achieve ecosystem functioning comparable to that of an unmodified ecosystem, therefore a reliable shorter-term method of assessing and monitoring ecosystem recovery is needed to ensure that recovery is following an appropriate trajectory. Soil microbes respond to environmental change relatively quickly, and shifts in microbial communities can reflect the current status of their environment. As well as potentially acting as ‘indicator communities’, microbes play an integral role in restoring ecosystem functions. On an active opencast mine on New Zealand's West Coast, three main restoration methods are used, differing in cost and restoration effort. They range from most expensive (1) vegetation direct transfer (VDT), to (2) biosolids-amended stockpiles that are spread and replanted, and (3) untreated stockpiles that are spread and replanted. We assessed the impacts of these methods on soil microbial communities by measuring microbial biomass, dehydrogenase activity, community level physiological profile (CLPP) and functional diversity as measured by carbon substrate utilisation, where restored sites were 5 years old or less. These measures were compared to an unmodified reference ecosystem in the same location. Microbial activity and biomass were highest in pristine habitats, followed by VDT and biosolids-amended soils, then untreated stockpile soil. When compared to all other treatments untreated stockpiled soils had significantly different CLPPs and significantly reduced microbial biomass and activity; microbial biomass was an order of magnitude lower than in pristine soils. Functional diversity and richness did not differ between pristine, VDT and biosolids-amended soils, but were higher than in untreated stockpiled soils. CLPPs did not differ between pristine habitat soil and VDT soil but biosolids-amended and untreated stockpiled soils were significantly different to pristine soil. This study has shown that soil microbial communities are a valuable tool to assess restoration progress, and that ecosystem restoration can begin in a relatively short time following investment in appropriate restoration strategy, ultimately benefiting recolonisation by plants and animals.     

长期施肥对双季稻田土壤微生物学特性的影响

为探明不同施肥处理对早稻和晚稻各个生育时期稻田土壤微生物生物量碳、氮和微生物熵的影响,以湖南宁乡长期定位试验为平台,应用氯仿熏蒸-K_2SO_4提取法和化学分析法系统分析了定位长达29年5种施肥处理之间(化肥、秸秆还田+化肥、30%有机肥+70%化肥、60%有机肥+40%化肥和无肥)双季稻田土壤微生物生物量碳、氮和微生物熵的差异。结果表明,早稻和晚稻各主要生育时期,长期施肥均能提高土壤微生物生物量碳、氮含量和微生物熵,各施肥处理土壤微生物生物量碳、氮含量和微生物熵均随水稻生育期推进呈先增加后降低的变化趋势,均于齐穗期达到最大值,成熟期达到最低值;其中,以60%有机肥和30%有机肥处理双季稻田土壤微生物生物量碳、氮含量和微生物熵均为最高,均显著高于其他处理,其大小顺序表现为60%有机肥30%有机肥秸秆还田化肥无肥。长期有机无机配施可以提高土壤微生物生物量碳、氮和微生物熵,有机肥与化肥配施对提高土壤肥力效果最好。土壤微生物生物量碳、氮及微生物熵可以反映土壤质量的变化,可作为评价土壤肥力的生物学指标。     

温带草原退化对土壤剖面微生物学特征的影响

【目的】草地退化已成为我国草原当前面临的最主要问题。土壤微生物量和土壤酶活性是反映土壤养分和土壤环境质量的重要指标。揭示退化程度对温带草原土壤剖面微生物学特征的影响规律。【方法】以内蒙古温带草原为研究对象,选取成熟自然草地以及中、重度退化草地和极度退化草地4种典型不同退化程度的草地,按不同土壤深度分层采样并进行土壤微生物量和土壤微生物酶活性的测定。【结果】表层土壤微生物生物量及其酶活性在不同退化样地中呈现出一致的趋势:成熟自然样地中度退化样地重度退化样地极度退化样地;10-20 cm土层土壤微生物学特征与表层的差异随着退化程度的加深逐渐减少,甚至在极度退化样地中10-20 cm层土壤微生物指标高于表层。【结论】表层土壤微生物生物量及其酶活性随着退化程度的加深而减少。同时,退化程度越严重,表层与10–20 cm土层之间土壤微生物学特征的差异越小。这一结果为评价草地退化程度提供了新思路,为温带草原的恢复和重建提供了重要的理论依据。     

Increased soil carbon storage through plant diversity strengthens with time and extends into the subsoil

Soils are important for ecosystem functioning and service provisioning. Soil communities and their functions, in turn, are strongly promoted by plant diversity, and such positive effects strengthen with time. However, plant diversity effects on soil organic matter have mostly been investigated in the topsoil, and there are only very few long-term studies. Thus, it remains unclear if plant diversity effects strengthen with time and to which depth these effects extend. Here, we repeatedly sampled soil to 1 m depth in a long-term grassland biodiversity experiment. We investigated how plant diversity impacted soil organic carbon and nitrogen concentrations and stocks and their stable isotopes ¹³C and ¹⁵N, as well as how these effects changed after 5, 10, and 14 years. We found that higher plant diversity increased carbon and nitrogen storage in the topsoil since the establishment of the experiment. Stable isotopes revealed that these increases were associated with new plant-derived inputs, resulting in less processed and less decomposed soil organic matter. In subsoils, mainly the presence of specific plant functional groups drove organic matter dynamics. For example, the presence of deep-rooting tall herbs decreased carbon concentrations, most probably through stimulating soil organic matter decomposition. Moreover, plant diversity effects on soil organic matter became stronger in topsoil over time and reached subsoil layers, while the effects of specific plant functional groups in subsoil progressively diminished over time. Our results indicate that after changing the soil system the pathways of organic matter transfer to the subsoil need time to establish. In our grassland system, organic matter storage in subsoils was driven by the redistribution of already stored soil organic matter from the topsoil to deeper soil layers, for example, via bioturbation or dissolved organic matter. Therefore, managing plant diversity may, thus, have significant implications for subsoil carbon storage and other critical ecosystem services.     

Effects of ecological restoration on beetle assemblages: results from a large-scale experiment in a Mediterranean steppe rangeland

Given that biological conservation cannot prevent the full range of negative impacts on biodiversity, ecological restoration is nowadays commonly acknowledged as a necessary tool for conservation purposes. Here, we report on an ecological rehabilitation project in the La Crau area (south-eastern France), beginning in 2009 when a former industrial orchard (357 ha) was rehabilitated into a Mediterranean rangeland. We assessed the effect of ecological rehabilitation and different additional restoration treatments on beetle assemblages. Seven treatments were considered: the reference steppe, the rehabilitated treatment alone, three additional experimental restoration treatments (soil transfer; nurse species seeding and hay transfer), the control and the edge between the steppe and the former industrial orchard area. All beetle families were considered. Beetles were sampled with pitfall traps for 3 years (2011–2013). Our major finding was a positive effect of soil transfer and nurse species seeding treatments, which promote the characteristic beetle composition of the reference steppe. Nevertheless, strong differences remain between the steppe and the various assessed treatments in terms of composition. Long-term monitoring should therefore now focus on particular beetle indicator species that could reflect the response of the overall characteristic beetle assemblage of the reference steppe.     

玉米 线辣椒套作系统中土壤养分与根际土壤微生物、酶活性的关系

采用玉米单作、线辣椒单作、玉米-线辣椒套作3种栽培模式,并在玉米-线辣椒套作的种间根部设3种不同隔离处理（膜隔、网隔和无隔）,研究了玉米-线辣椒套作系统中土壤生物因子与土壤养分的关系．结果表明：玉米-线辣椒套作具有明显优势;与两作物单作和玉米-线辣椒套作种间根区膜隔处理相比,玉米-线辣椒根区无隔和网隔处理复合群体中两作物根际土壤酶活性、微生物数量、土壤养分均显著提高;除有效镁与真菌种群数量、过氧化氢酶活性呈负相关外,其余速效养分与各生物因子均呈显著或极显著正相关．通径分析表明,该系统中促进有机质累积的主要生物因素是脲酶、过氧化氢酶、细菌和蛋白酶,蔗糖酶是影响碱解氮的最主要因子,脲酶是影响有效磷的最主要因子,细菌是影响有效钾的最主要因子,碱性磷酸酶、真菌只是选择性地对有机质的累积和氮、磷、钾有效养分的形成起作用,放线菌对土壤养分的直接作用系数为负,对土壤养分形成的作用较小．     

Heterogeneity of soil and plant N and C associated with individual plants and openings in North American shortgrass steppe

Small-scale spatial heterogeneity of soil organic matter (SOM) associated with patterns of plant cover can strongly influence population and ecosystem dynamics in dry regions but is not well characterized for semiarid grasslands. We evaluated differences in plant and soil N and C between soil from under individual grass plants and from small openings in shortgrass steppe. In samples from 0 to 5 cm depth, root biomass, root N, total and mineralizable soil N, total and respirable organic C, C:N ratio, fraction of organic C respired, and ratio of respiration to N mineralization were significantly greater for soil under plants than soil from openings. These differences, which were consistent for two sites with contrasting soil textures, indicate strong differentiation of surface soil at the scale of individual plants, with relative enrichment of soil under plants in total and active SOM. Between-microsite differences were substantial relative to previously reported differences associated with landscape position and grazing intensity in shortgrass steppe. We conclude that microscale heterogeneity in shortgrass steppe deserves attention in investigation of controls on ecosystem and population processes and when sampling to estimate properties at plot or site scales.     

Decomposition and stabilization of root litter in top- and subsoil horizons: what is the difference?

Mechanisms leading to high mean residence times of organic matter in subsoil horizons are poorly understood. In lower parts of the soil profile root material contributes greatly to soil organic matter (SOM). The objective of this study was to elucidate the decomposition dynamics of root-derived C and N in different soil depths during a 3 year field experiment and to examine the importance of different protection mechanisms as well as abiotic factors for the decomposition dynamics. Additionally, we assessed the effect of root litter addition on native SOM. Our conceptual approach included the exposure of litterbags with ¹³C and ¹⁵N labeled wheat root material mixed to loamy agricultural soil at three different soil depths (30, 60 and 90 cm). During the incubation period, we monitored soil temperature, humidity and the incorporation of root derived C and N into the soil microbial biomass and physical SOM fractions. Our results showed that abiotic decay conditions were better in subsurface horizons compared to the topsoil. Root litter addition significantly increased the size of microbial biomass in all three soil horizons. In the topsoil, root-derived C decomposition was significantly higher in the first 6 months of incubation compared to subsoil horizons. In 60 and 90 cm depths, a lag phase with development of soil microbial biomass seemed to be prevailing before decomposition was activated. For root-derived N, similar decomposition kinetics could be observed in top- and subsoil horizons. Despite of higher SOM contents, better soil structure and higher microbial activity in the topsoil horizon compared to subsoil horizons, the amounts of root-derived C and N remaining after 3 years were similar for all three depths. Most of the root-derived C and N was present as organo-mineral complexes or occluded in soil aggregates (oPOM), illustrating similar importance of these two protection mechanisms in all three soil depths. Addition of fresh root litter caused small losses of native soil C whereas native N was retained. We conclude that despite of similar SOM protection mechanisms, there are distinct differences in decomposition dynamics of root litter between top- and subsoil horizons. In the long run, the better abiotic decay conditions prevailing in subsoil horizons may compensate for their poorer physico-chemical characteristics.     

Distribution of soil organic matter between fractions and aggregate size classes in grazed semiarid steppe soil profiles

Grazed steppe ecosystems are discussed as one of the big global carbon sinks that may have the potential to sequester large amounts of atmospheric CO₂ and mitigate the effects of global change if grazing is abandoned or management improved. But until today, little is known about sequestration potentials and stabilisation mechanisms in complete soil profiles of semiarid grasslands and how these systems react to grazing cessation. We applied a combined aggregate size, density and particle size fractionation procedure to sandy steppe soils under different grazing intensities (continuously grazed = Cg, winter grazing = Wg, ungrazed since 1999 = Ug99, ungrazed since 1979 = Ug79). Higher inputs of organic matter in ungrazed treatments led to higher amounts of OC in coarse aggregate size classes (ASC) and especially in particulate organic matter (POM) fractions across all depth. These processes started in the topsoil and took more than 5 years to reach deeper soil horizons (>10 cm). After 25 years of grazing cessation, subsoils showed clearly higher POM amounts. We found no grazing-induced changes of soil organic matter (SOM) quantity in fine ASC and particle size fractions. Current C-loading of fine particle size fractions was similar between differently grazed plots and decreased with depth, pointing towards free sequestration capacities in deeper horizons. Despite these free capacities, we found no increase in current C-loading on fine mineral soil fractions after 25 years of grazing exclusion. Silt and clay fractions appeared to be saturated. We suppose empirical estimations to overestimate sequestration potentials of particle size fractions or climatic conditions to delay the decomposition and incorporation of OM into these particle size fractions. POM quality was analysed using solid-state ¹³C NMR spectroscopy to clarify if grazing cessation changed chemical composition of POM in different ASC and soil depths via changing litter quality or changing decomposition dynamics. We found comparable POM compositions between different grazing intensities. POM is decomposed hierarchically from coarse to fine particles in all soil depths and grazing cessation has not affected the OM decomposition processes. The surplus of OM due to grazing cessation was predominately sequestered in readily decomposable POM fractions across all affected horizons. We question the long-term stabilisation of OM in these steppe soils during the first 25 years after grazing cessation and request more studies in the field of long-term OM stabilisation processes and assessment of carbon sequestration capacities to consider deeper soil horizons.     

人工油松林（Pinus tabulaeformis）恢复过程中土壤微生物生物量C、N的变化特征

采用时空替代法,选取15a（PF15）、25a（PF25）、30a（PF30）的人工油松林作为样地,并选取灌丛作为参考植被,研究了植被恢复过程中土壤微生物生物量C、N以及土壤养分的变化特征,同时探讨了它们之间的相互关系。研究结果表明随着恢复的进行,土壤质量得到了改善,主要表现为有机碳、全氮、粘粒含量、土壤含水量的上升和pH值、容重的下降。土壤微生物生物量C、N分别在155.00~885.64mg/kg和33.73~237.40mg/kg的范围内变化。土壤微生物生物量C、N在植被恢复的初期显著低于灌丛,而后随着恢复的进行逐步增长。土壤微生物生物量C、N与植被恢复时间的相关性没有达到统计学上的显著水平,但是土壤微生物生物量C与土壤有机碳、全氮、全磷呈显著正相关,这表明植被恢复过程中土壤微生物生物量与土壤养分状况关系密切,植被恢复通过改善土壤养分状况间接地影响土壤微生物生物量的变化。Cmic/TOC在1.38%~4.75%的范围内变化。Cmic/TOC随着植被恢复不断下降,Cmic/TOC与植被恢复时间和土壤有机碳呈显著负相关,这表明植被恢复过程中,惰性有机质积累导致供应土壤微生物的活性有机质减少,Cmic/TOC同时受土壤有机质的数量和质量影响。     

26年长期施肥对土壤微生物量碳、氮及土壤呼吸的影响

研究长期小麦连作施肥条件下土壤微生物量碳、氮,土壤呼吸的变化及其与土壤养分的相关性。以陕西长武长期定位试验为平台,应用氯仿熏蒸-K2SO4提取法、碱液吸收法和化学分析法分析了长达26a不同施肥处理农田土壤微生物量碳、微生物量氮和土壤呼吸之间的差异及其调控土壤肥力的作用。长期施肥及种植作物,均能提高土壤微生物量碳、氮含量,尤其是施用有机肥,土壤微生物量碳、氮含量高于单施无机肥的处理,土壤呼吸量也提高15.91%—75.73%,而施用无机肥对于土壤呼吸无促进作用。土壤微生物生物量碳氮、土壤呼吸与土壤有机质、全氮呈极显著相关。长期有机无机肥配施可以提高土壤微生物量碳氮、土壤呼吸,氮磷肥与厩肥配施对提高土壤肥力效果最好。微生物量碳氮及土壤呼吸可以反映土壤质量的变化,作为评价土壤肥力的生物学指标。     

凋落物对土壤有机碳与微生物功能多样性的影响

森林凋落物是影响土壤微生物群落和有机碳含量的重要因素,但其作用的程度和机制尚不清楚,研究该问题对于分析森林生态系统碳循环和资源管理具有重要意义。研究凋落物去除与添加处理下土壤有机碳含量与土壤微生物对碳源利用的差异,明确凋落物去除与添加对土壤微生物群落代谢功能及其多样性的影响,探究不同处理下SOC含量变化的土壤微生物群落代谢机理。选取承德市雾灵山1405-1435 m海拔范围内核桃楸-蒙古栎混交林的表层土壤,采用室内培养结合Biolog-ECO方法,测定了培养第21天的土壤有机碳（soil organic carbon,SOC）含量及微生物群落的AWCD值、Shannon-Wiener多样性指数、Simpson优势度指数、McIntosh均匀度指数、Pielou丰富度指数,分析培养期内凋落物的不同处理下SOC含量与微生物功能多样性的变化特征。结果表明：1）不同凋落物处理对SOC含量与土壤微生物群落多样性具有显著影响（P<0.05）,DL > HL > NL > CK;2）不同凋落物处理下土壤微生物群落代谢活性和土壤微生物对碳源的利用程度具有显著差异（P<0.05）,碳水化合物类和氨基酸类是土壤微生物的主要碳源;3）不同处理的SOC含量与土壤微生物多样性具有正相关关系。双倍凋落物添加在短期内对土壤微生物多样性影响难以达到显著水平且在一定程度上对土壤微生物的代谢活性具有抑制作用,土壤微生物群落功能多样性对SOC含量具有重要影响。     

洞庭湖湿地土壤环境及其对退田还湖方式的响应

土壤物理、化学和生物学特性是构成土壤环境的主要组分,综合影响湿地生态系统的调蓄功能和演替恢复。本文以农田（水田和旱地）和自然湿地系统（苔草地和芦苇地）为对照,以3种退田还湖生态系统（种植杨树、芦苇和自然恢复）为研究对象,采用主成分和聚类分析,探索湿地土壤总体环境与生态系统演替过程的相关性。研究结果表明,土壤总体环境与生态系统恢复有很好的一致性。退田还湖为自然水域后,土壤环境的恢复接近于自然湿地系统,在3种退田还湖方式中恢复最好;杨树林地对土壤环境的恢复效果优于人工芦苇地,在一定程度上对湿地土壤环境有所改善,特别是对土壤有机质积累、土壤粘粒形成等过程的改善,但是其土壤环境与苔草等自然湿地发育的土壤仍然有较大差异;因子重要性分析表明水文情势是控制湿地土壤环境恢复的决定性因素,其次是人类干扰强度和方式。     

Microbial diversity and activity are increased by compost amendment of metal-contaminated soil

Unlike organic pollutants, heavy metals cannot be degraded and can constitute a persistent environmental hazard. Here, we investigated the success of different remediation strategies in promoting microbial diversity and function with depth in an acidic soil heavily contaminated with Cu, Pb and Zn. Remediation involved the incorporation of either a high- or a low-quality compost or inorganic fertilizer into the topsoil and monitoring of microbial activity and diversity with soil depth over a 4-month period. While changes in topsoil microbial activity were expected, the possible effects on the subsurface microbial community due to the downward movement of metals, nutrients and/or soluble organic matter have not been examined previously. The results showed that both compost additions, especially the low-quality compost, resulted in significantly increased bacterial and fungal diversity (as assessed by terminal restriction fragment length polymorphism) and activity compared with the inorganic and control treatments in the topsoil. Although phospholipid fatty acid profiling indicated that compost addition had promoted enhanced microbial diversity in the subsoil, no concomitant increase in subsoil microbial activity was observed, suggesting that amelioration of the heavy metals remained localized in the topsoil. We conclude that although composts can successfully immobilize heavy metals and promote ecosystem diversity/function, surface incorporation had little remedial effect below the surface layer over the course of our short-term trial.     

森林次生演替和土壤层次对微生物群落结构的影响

森林次生演替与生态系统结构和功能的动态变化密切相关。大多数研究主要关注植物群落以及土壤有机碳(SOC)的变化,然而土壤微生物群落如何响应森林次生演替还需要进一步探究。本研究以长白山森林次生演替序列(20、80、120、200和≥300年)和两个土壤层次为对象,采用磷脂脂肪酸微生物标志物,探究温带森林次生演替过程中地下微生物群落结构变化。森林次生演替改变了土壤微生物群落结构,主要归因于某些特定微生物类群的变化,演替前期革兰氏阴性菌和腐生真菌占主导,而在演替后期革兰氏阳性菌和丛枝菌根真菌占主导。另外,土壤有机质数量和质量差异是影响微生物群落结构和生物量的主要环境因素。森林演替前期和中期增加的SOC含量促进了微生物生物量,而演替后期增加的难分解芳香族有机组分抑制了微生物生物量合成。土壤层次间理化性质的差异导致微生物群落变化,有机质层高的SOC以及氮含量导致更多微生物生物量的合成。微生物群落在时间和空间尺度的变化及其驱动因素反映了生态系统结构和功能对环境变化的响应。     

藏北高寒草地土壤有机质化学组成对土壤蛋白酶和脲酶活性的影响

土壤酶作为生态系统的生物催化剂, 是土壤有机体的代谢驱动力, 在土壤物质循环和能量转化过程中起着重要作用。该研究以藏北5种不同类型高寒草地(高寒草甸、高寒草原、高寒草甸草原、高寒荒漠草原和高寒荒漠)为研究对象, 利用热裂解气质联用技术(Py-GC/MS)分析不同类型草地土壤有机质化学组成, 并建立其与土壤蛋白酶和脲酶活性之间的相互关系。结果表明, 5种高寒草地土壤(0-15 cm)的酶活性表现出一定差异性, 高寒荒漠草原土壤的脲酶活性显著高于蛋白酶活性, 而其余类型高寒草地的脲酶和蛋白酶活性之间的差异未达到显著水平; 蛋白酶活性在5种高寒草地土壤之间的差异显著, 而脲酶活性在5种草地土壤之间的差异未达到显著水平。相关分析发现, 土壤蛋白酶活性与土壤有机质烷烃、烯烃和芳香烃的相对丰度和糠醛:吡咯的值密切相关, 土壤脲酶活性与土壤有机质化学组成之间相关性未达到显著水平。综上所述, 高寒草地类型和土壤有机质化学组成是影响高寒草地土壤蛋白酶活性的重要因素, 而对土壤脲酶活性的影响均未达到显著水平, 其影响因素有待进一步深入的研究。     

植物、土壤及土壤管理对土壤微生物群落结构的影响

土壤微生物是土壤生态系统的重要组成部分,对土壤微生物群落结构多样性的研究是近年来土壤生态学研究的热点。本文综述了有关植物、土壤类型以及土壤管理措施对土壤微生物群落结构影响的最新研究结果,指出植物的作用因植物群落结构多样性、植物种类、同种植物不同的基因型,甚至同一植物不同根的区域而异;而土壤的作用与土壤质地和有机质含量等因素有关;植物和土壤类型在对土壤微生物群落结构影响上的作用存在互作关系。不同的土壤管理措施对土壤微生物群落结构影响较大,长期连作、大量的外援化学物质的应用降低了土壤微生物的多样性;而施用有机肥、免耕可以增加土壤微生物群落结构多样性,有利于维持土壤生态系统的功能。     

长期施肥对红壤和黑土硫形态演变的影响

以红壤和黑土肥力与肥料效益监测站土壤为研究对象,研究了长期(21年)不同施肥(不施肥对照、施用氮磷钾、氮磷钾配施有机肥)处理下,表层(0～20 cm)和亚表层(20～40 cm)土壤硫素形态组成、分布及演变规律.结果表明: 长期施用化肥及化肥配施有机肥处理下,表层土壤全硫比对照分别增加42%、33%(红壤)和6%、76%(黑土);除红壤氮磷钾处理外,亚表层土壤全硫受施肥影响较小,且明显低于相应表层土壤.有效硫和盐酸可提取态硫分别为红壤和黑土中的主要无机硫形态.施用化肥及化肥配施有机肥的红壤表层有效硫比对照分别增加了447%和102%,并促进了有效硫向亚表层的迁移、累积;而施用化肥及化肥配施有机肥处理的黑土表层有效硫仅比对照分别增加54%和93%,其对亚表层土壤有效硫的影响也不大.有机硫形态在两种土壤中都以酯键硫和残渣态硫为主.长期施肥影响下的表层和亚表层土壤中残渣态硫含量比对照分别增加了32%和55%以上;土壤中性质相对活跃的酯键硫和碳键硫受施肥影响不显著,而与土壤有机碳含量呈显著正相关关系(P<0.05).此外,长期施肥试验表明大气硫沉降对土壤硫素输入的影响值得重视.