长期不同施肥下水稻土甲烷氧化能力及甲烷氧化菌多样性的变化

稻田内源甲烷的氧化是稻田甲烷减排的重要途径。而甲烷氧化菌是土壤中甲烷氧化的主要施动者,在长期不同施肥条件下,土壤微生物群落的演变是否影响到土壤甲烷氧化菌群落结构及其活性,进而影响到田土壤CH4向大气的实际排放强度还不清楚。为此,选择太湖地区一个长期肥料试验的稻田土壤为研究对象,分析长期不同肥料施用对土壤甲烷氧化能力的影响及其与土壤中甲烷氧化菌群落结构变化的可能关系。结果表明,长期不同的施肥措施下稻田土壤对甲烷的氧化能力产生了明显差异,伴随着土壤中甲烷氧化菌（MOBI和MOBII）的基因群落多样性的显著变化。长期单一施用氮肥为主的化肥显著降低了土壤对甲烷的氧化能力,同时显著降低了稻田土壤甲烷氧化菌的多样性和丰富度;不同施肥下甲烷氧化菌多样性的变化与土壤的甲烷氧化能力的变化趋势相一致。因此,研究显示长期不同施肥处理下甲烷氧化菌群落结构的改变可能是引起水稻土甲烷氧化能力变化的一个主要因素,有机无机配合施用可以明显降低稻田土壤甲烷的大气释放潜能。但长期不同施肥处理下甲烷氧化菌活性的变化还有待于进一步研究。     

长期不同施肥下太湖地区黄泥土表土微生物碳氮量及基因多样性变化

农业管理措施影响下土壤微生物群落结构的变化是农业土壤质量研究的前沿问题。运用化学分析方法和 PCR- DGGE技术从土壤微生物碳氮量及基因多样性角度研究了长期不同施肥措施下太湖地区代表性水稻土 -黄泥土的表土微生物活性与分子多样性的变化。结果表明 ,施用化肥以及化肥和有机肥配施在提高土壤有机碳含量的同时 ,不仅提高了水稻土的微生物碳氮量 ,而且改变了微生物的群落结构 ;与长期单施化肥相比 ,长期化肥配施有机肥不仅显著提高了土壤微生物碳氮量 ,而且提高了土壤微生物的分子多样性 ;就土壤的微生物分子群落相似性来说 ,单施化肥下与未施肥下相近 ,而化肥配施秸秆下与化肥配施猪粪下接近 ,说明土壤的有机培肥对土壤微生物群落结构有重要影响。长期单施化肥下水稻产量的年际波动性显著大于化肥配施有机肥下 ,这进一步佐证了化肥配施有机肥显著促进了水稻土的生态系统初级生产力与较高的土壤生态系统稳定性。应用PCR- DGGE技术所揭示的微生物分子群落结构特点可以指示水稻土 10 a尺度的不同农业管理措施下的土壤质量变化     

包埋法固定化对硫氧化微生物菌群结构和功能的影响

【目的】为探讨包埋法固定化过程对硫氧化菌群硫化物去除能力及菌群微生物群落结构的影响,【方法】以聚乙烯醇-海藻酸钠-活性炭为载体,对硫氧化菌群进行了固定化,并采用富含硫化物的无机盐培养基,对比固定化与非固定化硫氧化菌群对硫化物的氧化去除能力。同时,利用PCR-DGGE技术,探讨硫氧化菌群在固定化前后以及在硫化物氧化去除过程中微生物群落结构变化。【结果】在对硫氧化菌群进行固定化之后,12 h之内对硫化物的最大去除能力从1000 mg/L下降为600 mg/L。硫氧化菌群的微生物群落结构发生了明显变化,但菌群中的硫氧化菌Catenococcus thiocycli未受影响,硫氧化菌Thioclava pacifica在菌群中的地位反而得到了强化。【结论】受制于底物在载体材料中的扩散迁移效率,硫氧化菌群对硫化物的氧化去除能力在固定化之后有所下降。由于不同微生物对固定化形成的微环境的适应能力以及对载体附着能力的不同,固定化对硫氧化菌群的微生物群落结构产生较大影响。     

模拟增温对青海湖鸟岛土壤微生物的影响

【背景】土壤微生物对其生存的微环境变化极为敏感,鸟岛作为湖滨湿地,对气候变化具有敏感性,但目前关于青海湖鸟岛的土壤微生物鲜有研究。【目的】探究气候变暖后青海湖鸟岛土壤微生物群落特征的变化。【方法】利用开顶箱模拟增温,通过高通量测序方法了解温度升高后土壤细菌及真菌的群落结构以及多样性的变化情况。【结果】温度的升高并未改变青海湖鸟岛土壤微生物的优势菌群,细菌优势菌群为变形菌门和酸杆菌门;真菌优势菌门为子囊菌门,优势菌纲为座囊菌纲。但增温改变了土壤微生物的群落结构,显著升高了拟杆菌门、蓝细菌门、Patescibacteria及球囊菌纲的相对丰度,显著降低了锤舌菌纲的相对丰度。土壤微生物群落的多样性指数也发生了变化,温度上升后微生物的ACE指数及Chao1指数均降低,细菌的Simpson指数及真菌的Shannon指数降低。【结论】青海湖鸟岛土壤微生物对温度升高的响应明显,增温改变了土壤细菌拟杆菌门、蓝细菌门、Patescibacteria的相对丰度及真菌的球囊菌纲、锤舌菌纲的相对丰度,降低了土壤微生物的多样性。     

水稻土中铁氧化物对产甲烷古菌群落结构的影响

产甲烷菌广泛分布在淹水水稻土等各种厌氧环境中,在全球气候变化、碳循环和能源等领域都发挥着重要的作用。研究发现,厌氧条件下,水稻土中铁氧化物的生物还原会抑制产甲烷菌的甲烷合成作用。然而,目前关于铁氧化物对产甲烷菌群落结构的影响报道较少。通过泥浆厌氧培养实验,向采集的水稻土中添加甲酸盐作为甲烷合成的底物(Control,CK处理),并设置添加水铁矿作为体系中唯一电子受体的处理组(Ferrihydrite,Fh处理)。培养结束后,与CK相比,添加水铁矿显著降低了古菌在总微生物群落中的占比,但对古菌群落的物种多样性和均一度没有显著影响;且两组处理中优势种均为操作分类单元(Operational taxonomic unit,OTU)2056和OTU 911(76%—80%)。这说明碳源相同时,产甲烷菌的群落结构不受铁氧化物的影响。本研究为探索土壤中微生物铁还原与碳循环耦合的分子机制奠定基础。     

生物质炭对水稻土团聚体微生物多样性的影响

生物质炭施用对土壤微生物群落结构的影响已有报道,但土壤团聚体粒组中微生物群落对生物质炭施用的响应的研究还相对不足。以施用玉米秸秆生物质炭两年后的水稻土为对象,采用团聚体湿筛法,通过高通量测序对土壤团聚体的微生物群落结构与多样性进行分析,结果表明:(1)与对照相比,生物质炭施用显著促进了大团聚体(2000—250μm)的形成,并提高了团聚体的稳定性。(2)不同粒径团聚体间微生物相对丰度存在显著差异。在未施生物质炭的处理(C0)中,随着团聚体粒径增大,变形菌门、子囊菌门、β-变形杆菌目、格孢腔菌目的相对丰度逐渐降低,而酸杆菌门、担子菌门、粘球菌目、类球囊霉目的相对丰度逐渐升高。(3)生物质炭施用显著改变了团聚体间的微生物群落结构。与C0处理相比,生物质炭施用处理的大团聚体中变形菌门、鞭毛菌门和β-变形杆菌目的相对丰度分别显著提高了14.37%、33.28%和33.82%;微团聚体(250—53μm)中酸杆菌门、子囊菌门和粘球菌目的相对丰度分别显著降低了20.15%、19.93%和17.66%;粉、黏粒组分(53μm)中担子菌门的相对丰度升高90.25%,而子囊菌门和鞭毛菌门的相对丰度分别降低12.15%和12.58%。由此可见,生物质炭不仅改变土壤团聚体组成和分布,同时伴随着土壤微生物群落结构的改变。     

根际微生物组介导的解淀粉芽孢杆菌FH-1对水稻的促生机制

【目的】利用大田实验和分子生物学技术进行水稻促生菌解淀粉芽孢杆菌(Bacillus amyloliquefaciens) FH-1改良土壤微生物组的研究,以初步了解解淀粉芽孢杆菌FH-1的促生机理,为微生物肥料的研制和应用提供理论基础。【方法】设置菌剂FH-1处理(FH)和空白对照(CK)的水稻大田实验,测定植物生理性状包括水稻株高、根长和穗长,并统计水稻的穗数、单穗粒数和千粒重;利用实时荧光定量PCR技术分析水稻根际土壤细菌的数量;利用16SrRNA基因高通量测序解析水稻根际土壤微生物的物种组成;进一步通过Pearson相关统计分析研究水稻-土壤-微生物之间的相互作用。【结果】与空白对照(CK)相比,菌剂FH-1处理(FH)中植物的株高、根长、穗长、单株穗数、单穗粒数、千粒重显著提高,但是土壤理化性质无显著性差异。菌剂FH-1处理(FH)对细菌总数量无显著影响,但是可显著降低微生物α多样性,显著提高土壤中的γ-变形菌纲、绿弯菌门,显著降低土壤中的β-变形菌纲、疣微菌门的丰度(P0.05),LEfSe分析显示菌剂FH-1处理(FH)土壤中富集的微生物有19个,主要包括绿弯菌门、PAUC34f、S035、4-29、芽孢杆菌纲、芽孢杆菌目、浮霉菌纲、A31、H39、S0208、Gemmatales、红螺菌目、HOC36、AKIW659、0319-6A21、生丝微菌科、红螺菌科、EB1003、HB2-32-21。相关性分析结果表明施加菌剂FH-1及其富集的相关物种与水稻植株的各个特性呈正相关。【结论】在水稻大田种植中施加微生物菌剂FH-1,可显著促进水稻生长,对土壤理化性质无显著影响,但可以显著改变微生物群落结构和功能,富集有益物种。因此我们推测解淀粉芽孢杆菌FH-1是通过调控根际微生物群落结构和功能促进水稻生长和发育。     

长期不同施肥措施下岩溶水稻土可培养细菌群落变化及其主要影响因素

【背景】施肥是目前提高作物产量的较优策略,不同的施肥措施在不同程度上影响土壤肥力和微生物群落结构。【目的】探究岩溶水稻土理化性质变化与细菌群落变化的对应关系,进而反映不同施肥措施对土壤可培养细菌群落的影响。最后选出最优施肥方案,为后续的合理施肥工作提供依据。【方法】对岩溶水稻土进行不施肥、常规施肥、常规施肥加绿肥3种施肥处理,通过对土壤理化性质、可培养细菌群落丰度及多样性变化的研究,探究在不同施肥措施下对岩溶水稻土壤细菌群落的影响。【结果】对比不施肥处理,常规施肥处理下土壤pH值和有机碳含量下降,结合大量研究结果证明,无机肥或氮肥的长期过量施加使土壤pH值下降,常规施肥加绿肥有利于有机碳的积累。分离纯化共得到164株菌,分别来自Actinobacteria、Bacteroidetes、Firmicutes和Proteobacteria。属水平上常规施肥配施绿肥较常规施肥组优势菌属Sphingomonas、Lysobacter的相对丰度增加。细菌群落多样性增加,出现Paenibacillus、Streptomyces和Pseudomonas等特有功能菌属。优势菌属Sphingopyxis、Lysobacter、Paenibacillus、Bosea、Streptomyces、Pseudomonas和Bacillus与TN存在显著正相关,在常规施肥加绿肥处理土壤中增加。【结论】常规施肥加绿肥处理下,固氮、溶磷等功能菌丰度增加,增加土壤肥力,保持土壤养分的可利用性,对作物的增产起重要作用。岩溶水稻土常规施肥配施绿肥处理的效果优于不施肥和常规施肥处理。     

长期施肥对黄土旱塬农田土壤微生物丰度的影响

以长武黄土高原农业生态试验站的长期定位试验为平台,通过荧光实时定量PCR (real-time PCR) 技术,研究不同施肥制度下的黄土旱塬农田土壤微生物群落丰度,揭示长期不同施肥制度对土壤微生物群落的影响规律.结果表明: 单施化肥处理细菌数量较CK裸地增加21％,古菌增加32％;化肥配施有机肥处理细菌数量增加37％,古菌数量增加36％.化肥配施有机肥处理显著增加了土壤细菌和古菌的丰度.30年长期施氮肥处理导致氨氧化细菌(AOB)的增幅达7.13倍,而氨氧化古菌(AOA)的增幅仅为0.2倍.AOB对施肥的响应程度较高,尤其是对氮肥具有较高的敏感性.与单施氮肥和氮肥混施有机肥处理相比,施磷肥处理显著增加了固氮酶铁蛋白和甲烷氧化菌含量,撂荒地的固氮酶铁蛋白、亚硝酸还原酶和甲烷氧化菌含量显著高于耕作土壤.结合土壤基本理化性质的相关性分析结果,pH、全氮和有机碳含量是影响土壤微生物群落丰度的重要因子.总之,长期施肥显著改变了黄土旱塬农田土壤各微生物丰度,不同施肥模式、耕作方式对微生物群落丰度具有显著影响.     

氮添加对黄土丘陵区油松人工林根际土壤微生物群落结构的影响

中国南方及中部为高氮沉降区(～35 kg·hm^-2·a^-1),氮沉降量向西北依次递减(～7.55 kg·hm^-2·a^-1).黄土高原区历经几十年的退耕还林还草而面貌一新,但该区域人工林土壤微生物群落结构对氮素添加响应的研究还鲜有报道.本研究以黄土丘陵区不同林龄油松人工林为研究对象,应用Illumina HiSeq测序技术对细菌16S rDNA和真菌ITS进行序列测定与分析,探讨根际土壤细菌和真菌群落结构组成对土壤氮添加(施用量为200 kg N·hm^-2·a^-1纯氮)的响应,旨在探究我国西北黄土丘陵区油松人工林根际土壤微生物多样性及群落结构对定量氮添加的响应.结果表明: 氮添加显著增加了25年龄林地细菌和真菌Shannon多样性,显著增加了40年龄林地细菌丰度指数.氮添加显著增加了40年龄林地拟杆菌门的相对丰度和25年龄林地酸杆菌门及接合菌门的相对丰度,但显著降低了40年龄林地奇古菌门的相对丰度.非度量多维尺度分析结果显示,氮添加对土壤细菌群落结构组成的影响程度大于真菌,对25年龄林地微生物群落结构组成的影响程度大于40年龄林地.表明不同林龄油松人工林根际土壤微生物的多样性及群落结构对土壤氮添加响应具有差异性.相对于真菌群落结构组成,细菌群落结构组成对氮添加更敏感;相对于40年龄林地,25年龄林地根际土壤微生物的群落结构组成对氮添加更敏感.因此,黄土高原区人工林地生态系统演替到一定阶段(40年左右),比幼龄林地生态系统更能承受外界较大的氮添加扰动.     

Alteration and resilience of the soil microbial community following compost amendment: effects of compost level and compost-borne microbial community

Compost amendment has been reported to impact soil microbial activities or community composition. However, little information is available on (i) to what extent compost amendment concurrently affects the activity, size and composition of soil microbial community, (ii) the relative effect of the addition of a material rich in organic matter versus addition of compost-borne microorganisms in explaining the effects of amendment and (iii) the resilience of community characteristics. We compared five treatments in microcosms: (i) control soil (S), (ii) soil + low level of compost (Sc), (iii) soil + high level of compost (SC), (iv) sterilized soil + high level of compost [(S)C] and (v) soil + high level of sterilized compost [S(C)]. The actual C mineralization rate, substrate-induced respiration, size of microbial community (biomass and heterotrophic cells number), and structure of total microbial (phospholipid fatty acids) and bacterial (automated ribosomal intergenic spacer analysis, A-RISA) communities were surveyed during 6 months after amendment. Our results show that (i) compost amendment affected the activity, size and composition of the soil microbial community, (ii) the effect of compost amendment was mainly due to the physicochemical characteristics of compost matrix rather than to compost-borne microorganisms and (iii) no resilience of microbial characteristics was observed 6-12 months after amendment with a high amount of compost.     

Molecular and Functional Assessment of Bacterial Community Convergence in Metal-Amended Soils

Species diversity and the structure of microbial communities in soils are thought to be a function of the cumulative selective pressures within the local environment. Shifts in microbial community structure, as a result of metal stress, may have lasting negative effects on soil ecosystem dynamics if critical microbial community functions are compromised. Three soils in the vicinity of a copper smelter, previously contaminated with background, low and high levels of aerially deposited metals, were amended with metal-salts to determine the potential for metal contamination to shape the structural and functional diversity of microbial communities in soils. We hypothesized that the microbial communities native to the three soils would initially be unique to each site, but would converge on a microbial community with similar structure and function, as a result of metal stress. Initially, the three different sites supported microbial communities with unique structural and functional diversity, and the nonimpacted site supported inherently higher levels of microbial activity and biomass, relative to the metal-contaminated sites. Amendment of the soils with metal-salts resulted in a decrease in microbial activity and biomass, as well as shifts in microbial community structure and function at each site. Soil microbial communities from each site were also observed to be sensitive to changes in soil pH as a result of metal-salt amendment; however, the magnitude of these pH-associated effects varied between soils. Microbial communities from each site did not converge on a structurally or functionally similar community following metal-salt amendment, indicating that other factors may be equally important in shaping microbial communities in soils. Among these factors, soil physiochemical parameters like organic matter and soil pH, which can both influence the bioavailability and toxicity of metals in soils, may be critical.     

The Impact of Biofumigation and Chemical Fumigation Methods on the Structure and Function of the Soil Microbial Community

Biofumigation (BIOF) is carried out mainly by the incorporation of brassica plant parts into the soil, and this fumigation activity has been linked to their high glucosinolate (GSL) content. GSLs are hydrolyzed by the endogenous enzyme myrosinase to release isothiocyanates (ITCs). A microcosm study was conducted to investigate the effects induced on the soil microbial community by the incorporation of broccoli residues into soil either with (BM) or without (B) added myrosinase and of chemical fumigation, either as soil application of 2-phenylethyl ITC (PITC) or metham sodium (MS). Soil microbial activity was evaluated by measuring fluorescein diacetate hydrolysis and soil respiration. Effects on the structure of the total microbial community were assessed by phospholipid fatty acid analysis, while the impact on important fungal (ascomycetes (ASC)) and bacterial (ammonia-oxidizing bacteria (AOB)) guilds was evaluated by denaturating gradient gel electrophoresis (DGGE). Overall, B, and to a lesser extent BM, stimulated microbial activity and biomass. The diminished effect of BM compared to B was particularly evident in fungi and Gram-negative bacteria and was attributed to rapid ITC release following the myrosinase treatment. PITC did not have a significant effect, whereas an inhibitory effect was observed in the MS-treated soil. DGGE analysis showed that the ASC community was temporarily altered by BIOF treatments and more persistently by the MS treatment, while the structure of the AOB community was not affected by the treatments. Cloning of the ASC community showed that MS application had a deleterious effect on potential plant pathogens like Fusarium, Nectria, and Cladosporium compared to BIOF treatments which did not appear to inhibit them. Our findings indicate that BIOF induces changes on the structure and function of the soil microbial community that are mostly related to microbial substrate availability changes derived from the soil amendment with fresh organic materials.     

Long-term effects of organic amendments on the recovery of plant and soil microbial communities following disturbance in the Canadian boreal forest

Background and Aims

Ecosystem recovery following disturbance requires the reestablishment of key soil biogeochemical processes. This long-term 7 year study describes effects of organic material, moisture, and vegetation on soil microbial community development in the Athabasca Oil Sands Region of Western Canada.

Methods

Phospholipid fatty acid analysis was used to characterize and compare soil microbial community composition and development on reclaimed and natural forest sites. Additionally, we conducted a laboratory moisture manipulation experiment.

Results

The use of forest floor material as an organic amendment resulted in a greater percent cover of upland vegetation and placed the soil microbial community on a faster trajectory towards ecosystem recovery than did the use of a peat amendment. The soil microbial composition within the reclaimed sites exhibited a greater response to changes in moisture than did the soil microbial communities from natural sites.

Conclusion

Our research shows that the use of native organic amendment (forest floor) on reclaimed sites, and the associated establishment of native vegetation promote the development of soil microbial communities more similar to those found on natural forest sites. Additionally, soil microbial communities from natural sites may be more resistant to changes in soil moisture than those found on reclaimed sites.     

Do Botanical Pesticides Alter the Structure of the Soil Microbial Community?

The effects of synthetic pesticides on the soil microbial community have been thoroughly investigated in the past mostly by culture-dependent methods and only few recent studies have used culture-independent approaches for this purpose. However, it should be noted that most of these studies have been conducted in microcosms where the soil microbial community is exposed to unrealistic concentrations of the pesticides, providing an unrealistic exposure scheme for soil microorganism. On the other hand, little is known regarding the potential impact of botanical pesticides on the soil microbial community. Therefore, a laboratory study and a field study were conducted to investigate the effects of synthetic (metham sodium [MS], sodium tetrathiocarbonate [SoTe], and fosthiazate) and botanical pesticides (azadirachtin, quillaja, and pulverized Melia azedarach fruits [PMF]) on the soil microbial community using phospholipid fatty acids (PLFA) analysis. Principal component analysis (PCA) on the results of the laboratory study indicated that the application of PMF resulted in significant changes in the soil microbial community. This was obvious by the proportional increase in the abundance of fatty acids 18:1ω9cis, 18:1ω9trans, which are common in gram-negative bacteria and saprotrophic fungi, and 18:2ω6,9, which is a fungal indicator. This response was attributed to the release of copious amounts of organic carbon and nutrients in the soil by the PMF. On the other hand, MS inhibited fungi and gram-negative bacteria, while fosthiazate and the botanical pesticides quillaja and azadirachtin did not impose significant changes in the soil microbial community. Similar results were obtained by the field study where application of the fumigants MS and SoTe significantly altered the structure of the soil microbial community with the former having a more prominent effect. Fosthiazate imposed mild changes in the soil microbial community, whereas quillaja and azadirachtin again did not show a significant effect. Overall, botanical pesticides, at their recommended dose, did not alter the structure of the soil microbial community compared to synthetic nonfumigant and fumigant pesticides which induced significant changes.     

Microflora of technogenous wastes characterised by fatty acid profiling

Fatty acid methyl ester (FAME) profiles obtained directly in situ have been used to estimate microbial community structure in different technogenous wastes. The effect of nutrients added, simulating the effect of plant-derived exudates on the indigenous microflora in the heaps during the reclamation process, was also studied in microcosms. The wastes such as coal-mine spoil, non-ferrous metallurgical slag and coal fly-ash were characterised by a poorly developed microflora as compared to a typical sandy loam soil. However, the most similar to the soil was the community structure in the coalmine spoil. The high content of 18: 2omega6,9 found in the metallurgical slag indicated the domination of fungi in this waste. In contrast, representatives of the Cytophaga-Flavobacterium group dominated the coal fly-ash, for which 16:1omega5c was used as the marker acid. The waste amendment resulted in changes of FAME profiles obtained. However, the changes were site-specific, indicating response of particular microbial groups to the added nutrients.     

生物炭对农田土壤微生物生态的影响研究进展

生物炭作为新型土壤改良剂在国内外环境科学等领域受到广泛的关注.关于生物炭对土壤理化性质的改良研究较早,目前虽然已深入到土壤微生物生态的领域,但是大多数将土壤理化性质与土壤微生物生态分开考虑,缺乏对二者相互作用的系统评述.本文总结了施用生物炭后土壤理化性质的改变与土壤微生物群落变化之间的相互关系:生物炭不仅能够提高土壤pH值、增强土壤的持水能力、增加土壤有机质等,而且会影响土壤微生物的群落结构、改变细菌和真菌的丰度;施用生物炭后,土壤环境和土壤微生物之间互相影响互相制约,共同促进了土壤微生物生态系统的改良.本文旨在为生物炭改良农田土壤微生态的深入研究提供新的思路,从生态系统的角度促进生物炭环境效应影响的研究,使生物炭的应用更具有科学性和有效性,并对生物炭在相关领域的应用进行了展望.     

Monitoring Soil Ecosystem Recovery Following Bioremediation of a Terrestrial Crude Oil Spill With and Without a Fertilizer Amendment

The effect of fertilizer as an amendment in the bioremediation of a terrestrial crude oil spill has been investigated in terms of the subsequent recovery of the soil ecosystem following bioremediation. Two different spills in the same area with different initial hydrocarbon concentrations (33,500 mg kg^-1 and 4,800 mg kg^-1) were compared. At the higher initial hydrocarbon concentration fertilizer addition increased the rate of bioremediation (first-order rate constant of 0.0033 days-1 with fertilizer amendment vs. 0.0020 days-1 without) and resulted in more rapid recovery of soil bacteria (numbers, community structure, diversity) and nematodes (trophic diversity and community structure). The effect of the fertilizer amendment was more significant at the higher initial concentration of crude oil hydrocarbons, presumably due to greater depletion of soil nutrient pools in the absence of the amendment. A second objective of this work was to identify sensitive and cost-effective ecological indicators useful for monitoring the recovery of soil ecosystems impacted by crude oil. Ecological indicators used included: microbial numbers, community structure, and activity as revealed by biomarker analysis (phospholipid fatty acids); nitrogen availability; nematode numbers and community structure (trophic groups and colonizer-persister classes); and ultimately, plant cover and diversity. All ecological indicators investigated were sensitive to disturbances in the soil food web in a hydrocarbon-impacted site. However, nematode community structure analysis offered the greatest sensitivity coupled with low cost and readily available sources for the analysis.     

有机物料种类及腐熟水平对土壤微生物群落的影响

应用Biolog方法研究了温室盆栽番茄条件下,施用不同种类及不同腐熟水平的有机物料对土壤微生物群落的影响,施用有机物料60d后取土分析土壤微生物群落多样性及土壤微生物对Biolog微平板中胺、氨基酸、糖、羧酸、聚合物和其它类碳源的利用情况,结果表明,施用有机物料可提高土壤微生物群落多样性,施用新鲜酒糟的多样性指数略高于施用腐熟10d酒糟,牛粪不同腐熟水平对多样性影响显著,且对多样性具有正向或负向的影响;对照和施用酒糟的土壤微生物对聚合物的利用率高于施用牛粪处理,施用新鲜物料处理的土壤微生物对聚合物的利用率高于施用腐熟物料处理。     

Priming effect after glucose amendment in two different soils evaluated by SIR- and PLFA-technique

This study investigated the metabolic and structural effects of adding glucose to the top soils of a contaminated sandy Eutric Cambisol and an uncontaminated silty Haplic Chernozem during substrate-induced respiration (SIR) measurement. We hypothesized that glucose amendment causes microbial community shifts. To indicate changes of the microbial structure during SIR measurement, we have evaluated the microbial community structure using phospholipid fatty acid (PLFA) analysis on soil samples immediately before they were enclosed in SIR apparatus (Start), after the equilibrium of basal respiration had been reached (Con-0), 8 h later (Con-8), and on the other hand immediately after adding glucose (Glu-0), and 8 h after that (Glu-8).The accumulated PLFA content of Start, Con-0 and Con-8 was of the same order of magnitude with no significant differences among them in the contaminated sandy Eutric Cambisol. In contrast, PLFA-biomass of the Glu-0 sample was only 52% of that measured in the Start. Furthermore, the PLFA-biomass was reduced even more drastically to 20% compared to the original Start value in Glu-8. The reduction of PLFA-microbial biomass after glucose amendment was accompanied by the inverse reaction of basal respiration. The PLFA profiles were dominated by the group of saturated fatty acids in the case of Start, Con-0 and Con-8, but by unsaturated fatty acids in the Glu-0 and Glu-8. In contrast to these results, the uncontaminated silty Haplic Chernozem showed no significant differences between Start, Con-0 and Glu-0 but a 243% and a 274% higher PLFA content of Con-8 and Glu-8 compared to the Start, respectively.The findings of triggered metabolic activities indicate that the microflora of these soils is affected and that PLFA analysis reflects a shift in the soil microbial community after adding glucose. We hypothesized that this shift from slow-growing microbial oligotrophs with low substrate needs to fast-growing copiotrophs with high substrate demands might be caused by the glucose added. Structural differences of the microbial community before and after glucose amendment should be taken into consideration when interpreting the metabolic SIR results in future.