采煤沉陷区不同造林树种恢复土壤酚酸物质对土壤微生物的影响

酚酸物质是影响微生物群落和结构的最重要因子之一,研究酚酸物质在不同造林树种土壤中的变化规律及其与微生物群落结构的关系,有助于更好地了解和揭示采煤沉陷区恢复造林条件下微生物群落变化的机制.本研究在双鸭山宝山采煤沉陷区的撂荒地基础上营造三针一阔(红松、落叶松、樟子松和杨树)人工林,测定这4种造林地土壤酚类物质、11种酚酸物质和微生物群落结构.结果表明: 复合态酚含量总体表现为人工林显著高于撂荒地,其中,落叶松人工林和杨树人工林的复合态酚含量较高,落叶松人工林和红松人工林的总酚含量显著高于撂荒地,红松人工林的水溶性酚含量显著高于撂荒地;在11种酚酸物质中,阿魏酸、松香酸、β-谷甾醇、齐墩果酸、莽草酸、亚油酸和硬脂酸的含量在人工林土壤中较高.土壤酚类物质与土壤微生物生物量不存在显著的相关关系,个别的酚酸物质与土壤微生物的相关关系显著,其中,阿魏酸、松香酸和β-谷甾醇对土壤微生物生物量有明显的促进作用,与真菌和真菌/细菌存在显著的正相关关系.杨树人工林的酚酸物质含量较高,说明营造杨树人工林对采煤沉陷区的土壤恢复有益.     

晋西北黄土高原丘陵区不同土地利用方式下土壤碳氮储量

对晋西北黄土高原丘陵区杨树-小叶锦鸡儿人工林、小叶锦鸡儿人工灌丛、杨树人工林、撂荒地和农田5种土地利用方式下土壤碳氮储量进行研究.结果表明: 不同土地利用方式下土壤碳氮含量、碳氮密度和碳氮储量存在显著差异.5种土地利用方式0～20 cm表层土壤碳氮含量和碳氮密度均显著大于20～40 cm和40～60 cm土层.5种土地利用方式同一土层碳氮含量和碳氮密度大小为: 杨树-小叶锦鸡儿人工林>小叶锦鸡儿人工灌丛>杨树人工林>撂荒地>农田;0～60 cm土层土壤有机碳储量大小为:杨树-小-叶锦鸡儿人工林(30.09 t·hm^-2)>小叶锦鸡儿人工灌丛(24.78 t·hm^-2)>杨树人工林(24.14 t·hm^-2)>撂荒地(22.06 t·hm^-2)>农田(17.59 t·hm^-2);土壤氮储量与有机碳储量变化规律相似,杨树-小叶锦鸡儿人工林0～60 cm土层土壤氮储量(4.94 t·hm^-2)最高,其次是小叶锦鸡儿人工灌丛(3.53 t·hm^-2)、杨树人工林(3.51 t·hm^-2)和撂荒地(3.40 t·hm^-2),农田土壤氮储量(2.71 t·hm^-2)最低.杨树-小叶锦鸡儿人工林和小叶锦鸡儿人工灌丛是晋西北黄土高原丘陵区植被建设和生态恢复过程中较好的两种土地利用方式.     

土地利用方式对土壤活性碳库和碳库管理指数的影响

以江西省安福县15年利用历史的撂荒地和3种林地(毛竹人工林、木荷次生林、杉木人工林)等土地利用方式为研究对象,探讨土地利用方式对活性有机碳库以及碳库管理指数的影响。结果表明:(1)不同样地土壤活性有机碳库的大小顺序为毛竹人工林(14.56 t·hm-2)木荷次生林(14.41 t·hm-2)杉木人工林(13.39 t·hm-2)撂荒地(9.53 t·hm-2),3种林地均显著高于撂荒地。(2)土地利用方式转变成林地后土壤总有机碳含量、活性有机碳含量、稳定态碳含量、碳库指数均有大幅度提高,木荷次生林土壤碳库活度、碳库活度指数值均最大,毛竹人工林氧化稳定系数最大,以撂荒地作为参考计算出不同土地利用方式土壤碳库管理指数值,排列顺序为:木荷次生林(184.61)毛竹人工林(172.58)杉木人工林(150.50)撂荒地(100)。(3)林地对土壤更具有培肥作用,处于良性管理状态,尤其以木荷次生林最佳。     

东北温带次生林与落叶松人工林的土壤呼吸

2006年5—10月,使用Li-6400-09土壤呼吸系统测定了黑龙江省帽儿山地区温带次生林转化为落叶松人工林后土壤呼吸速率(Rs)的变化.结果表明:次生林与落叶松人工林土壤呼吸速率的日变化均呈单峰型曲线,与地温的日变化趋势相似.测定期间内,次生林和落叶松人工林Rs的变化范围分别为0.43~7.26μmol CO2.m-2.s-1和0.63~4.70μmol CO2.m-2.s-1,最大值出现在7—8月,最小值出现在10月.5—8月,次生林的Rs明显高于落叶松人工林.次生林和落叶松人工林枯落物层呼吸速率的季节变化范围分别为-0.65~1.26μmol CO2.m-2.s-1和-0.43~0.47μmol CO2.m-2.s-1.两林分中的Rs与土壤温度均呈明显的指数相关,且与5 cm深地温相关最紧密.用5 cm地温估算的次生林和落叶松人工林Q10分别为3.61和3.07.次生林的Rs与10~20 cm土壤含水率相关显著,而落叶松人工林的Rs与土壤含水率无明显相关.     

科尔沁沙地樟子松人工林土壤真菌共现网络及其与土壤因子的关系

为揭示科尔沁沙地樟子松(Pinus sylvestris var.mongolica)人工林土壤真菌间相互作用，以不同林龄(中龄、近熟和成熟)、不同土层(0—10和10—20 cm)樟子松人工林土壤为研究对象，以未造林地为对照样地，采用分子生态网络分析法，基于随机矩阵理比较分析樟子松人工林土壤真菌网络特征及其影响因素。研究结果表明：(1)中龄林到近熟林阶段，科尔沁沙地樟子松人工林土壤真菌网络平均连通度增大，平均路径长减小，网络愈加复杂，而近熟林到成熟林阶段则相反，网络愈加简单；不同土层间，10—20 cm土层土壤真菌平均路径长度小于0—10 cm土层，平均连通度和聚类系数大于0—10 cm土层，10—20 cm较0—10 cm土壤真菌间相互联系更为密切；与樟子松人工林相比，未造林地土壤真菌网络中的平均连通度略低于近熟林，平均路径长低于樟子松人工林，未造林地土壤真菌群落更不稳定。(2)中龄、近熟和成熟樟子松人工林土壤真菌关键菌种分别为Guehomyces sp.、Oidiodendron sp.和Pseudeurotium sp.,未造林地关键菌种为Alphamyces sp.。在0—1...     

煤矸山复垦林地和草地土壤微生物多样性和群落组成的差异及其影响因素

以山西省长治市潞安矿区煤矸山复垦多年的林地和草地为对象,采用磷脂脂肪酸法(phospholipid fatty acid,PLFA)研究2种复垦样地0~10和10~20 cm土层土壤微生物多样性和群落组成状况以及土壤环境因子对微生物群落组成的影响。结果表明:(1)草地0~10和10~20 cm土层土壤微生物丰富度指数(S)、Shannon指数(H)均大于林地(P0.05),但2种样地Pielou均匀度指数(E)无显著差异。(2)林地在0~10和10~20 cm土层土壤微生物总PLFAs含量、真菌PLFAs含量、放线菌PLFAs含量、革兰氏阳性菌PLFAs含量以及革兰氏阳性菌/革兰氏阴性菌、真菌/细菌均高于草地(P0.05);但细菌PLFAs含量和革兰氏阴性菌PLFAs含量在2土层中表现不同,林地0~10 cm土层高于草地(P0.05),10~20 cm土层则低于草地。(3)主成分分析表明,土壤微生物群落结构组成受复垦类型的显著影响。冗余分析表明,土壤理化性质对微生物PLFAs含量产生影响,其中土壤有效磷(AP)、pH值和阳离子交换量(CEC)是影响微生物群落组成的主要因子,并且AP和CEC与土壤微生物PLFAs含量呈正相关,pH值与之呈负相关。     

Tree species influences soil microbial community diversity but not biomass in a karst forest in southwestern China

中国西南喀斯特森林树种对土壤微生物群落多样性和生物量的影响 陆地生态系统中植物种对土壤微生物群落结构的影响不一，而喀斯特生态系统中植物种对土壤微生物群落结构影响的研究尚未见报道。本研究利用磷酸脂肪酸(PLFA)法，分析了黔中高原型喀斯特常绿落叶阔叶混交林5个优势树种—窄叶石栎(Lithocarpus confinis Huang)、圆果化香(Platycarya longipes Wu)、滇鼠刺(Itea yunnanensis Franch.)、安顺润楠(Machilus cavaleriei H. Lév.)、云贵鹅耳枥(Carpinus pubescens Burkill)—与土壤理化性质对土壤微生物群落组成和生物量的影响。在测试的212个土壤样品 中共检测出132种PLFA，每个样品土壤微生物平均PLFA数量和生物量分别为65.97和11.22 µg g^–1。土壤表层(0–10 cm)的土壤微生物PLFA数量与下层(10–20 cm)土壤接近，但前者土壤微生物生物量显著高于后者(P < 0.05)。树种影响土壤微生物PLFA数量，但对土壤微生物生物量没有影响。云贵鹅耳枥附近的土壤微生物PLFA数量显著高于其他树种(P < 0.05)，而其他树种土壤微生物PLFA数量接近。土壤微生物 生物量与表层土壤的理化性质无显著相关，但与下层土壤的有机碳、全氮和全磷含量呈显著正相关 (P < 0.05)。总之，黔中高原型喀斯特森林真菌/细菌生物量比率低，微生物总生物量低，但微生物群落多样性高。树种对土壤微生物群落多样性产生影响。     

亚热带森林转换对土壤微生物呼吸及其熵值的影响

土壤微生物呼吸及其熵值是表征土壤质量变化的敏感性指标,不仅能衡量土壤微生物碳利用效率,还能揭示土壤有机碳的变化。通过比较亚热带米槠天然林转换为马尾松人工林和杉木人工林后土壤微生物呼吸速率、土壤微生物生物量碳以及微生物熵、代谢熵的差异,研究亚热带森林转换对土壤微生物碳利用效率的影响。研究结果显示:(1)与天然林相比,马尾松人工林0—10 cm土壤微生物呼吸速率上升32%(P0.05),马尾松人工林和杉木人工林10—20 cm土壤微生物呼吸速率分别下降26%和24%(P0.05);但在20—40 cm土层和40—60 cm土层,天然林土壤微生物呼吸速率比马尾松人工林分别高50%和43%;(2)马尾松人工林和杉木人工林0—10 cm土层土壤微生物生物量碳(MBC)比天然林分别下降19%和40%(P0.05),但马尾松人工林10—20 cm土壤MBC上升29%(P0.05);(3)人工林表层土壤微生物熵与天然林没有显著差异,但与天然林相比,杉木人工林和马尾松人工林20—40 cm土层土壤微生物熵分别下降51%和71%(P0.05),40—60 cm分别下降52%、66%(P0.05)。土壤微生物代谢熵的变化主要发生在0—10 cm土层,马尾松人工林和杉木人工林分别比天然林增加38%和29%(P0.05),在深层土壤,3种林分微生物代谢熵没有显著差异。亚热带森林转换导致表层土壤微生物碳利用效率下降,深层土壤易分解碳在总有机碳库中占比下降,有机碳可利用程度降低。     

大兴安岭重度火烧迹地恢复后土壤磷形态与解磷细菌分布特征

为了探讨大兴安岭重度火烧迹地恢复后土壤不同磷形态含量、解磷细菌群落结构的差异及两者之间的关系,以人工恢复(樟子松人工林、落叶松人工林)、人工促进天然恢复(次生林)以及天然恢复(天然次生林)的林地土壤为研究对象,采用Sui等修正的Hedley磷素分级法对根际土壤和0～10、10～20 cm非根际土壤进行磷素分级测定,并用高通量测序法得到土壤解磷细菌种群丰度。结果表明: 0～10 cm非根际土壤水溶性磷(H₂O-P_i)、碳酸氢钠无机磷(NaHCO₃-P_i)、碳酸氢钠有机磷(NaHCO₃-P_o)及根际土壤NaHCO₃-P_o含量表现为落叶松人工林>樟子松人工林>天然次生林>次生林。10～20 cm非根际土壤H₂O-P_i、NaHCO₃-P_i、NaHCO₃-P_o及根际土壤H₂O-P_i、NaHCO₃-P_i含量表现为落叶松人工林>樟子松人工林>次生林>天然次生林。不同林分根际与非根际土壤H₂O-P_i、NaHCO₃-P_i和NaHCO₃-P_o含量的比值(R/S)均大于1。中等活性氢氧化钠磷(NaOH-P)包括氢氧化钠无机磷(NaOH-P_i)和氢氧化钠有机磷(NaOH-P_o)。在0～10 cm非根际土壤及根际土壤中NaOH-P含量表现为落叶松人工林>天然次生林>次生林>樟子松人工林,在10～20 cm非根际土壤中表现为落叶松人工林>樟子松人工林>次生林>天然次生林。土壤NaOH-P存在明显的根际效应。酸溶性磷(HCl-P)包括酸溶性无机磷(HCl-P_i)和酸溶性有机磷(HCl-P_o)。在0～10 cm非根际土壤中HCl-P含量表现为落叶松人工林>天然次生林>樟子松人工林>次生林,在10～20 cm非根际及根际土壤中表现为落叶松人工林>樟子松人工林>天然次生林>次生林。土壤残留磷(residual-P)含量对林地恢复方式不敏感。各林分土壤主要解磷细菌均为慢生根瘤菌属、链霉菌属、伯克霍尔德菌属和芽孢杆菌属。樟子松人工林和落叶松人工林土壤解磷细菌丰度显著高于次生林和天然次生林。冗余分析表明,解磷细菌与不同磷形态之间相关性各异。在现阶段来看,人工恢复更有利于提高土壤磷的有效性和增加解磷细菌的丰度。     

氮肥添加对高寒藏嵩草(Kobresia tibetica)沼泽化草甸和土壤微生物群落的影响

以藏嵩草沼泽化草甸为研究对象,利用磷脂脂肪酸(PLFA)技术,研究连续6年N素添加对地上植被群落数量特征、土壤微生物群落结构的影响。结果表明:①藏嵩草沼泽化草甸群落生物量、枯枝落叶对施肥处理无明显响应,且莎草科植物对土壤氮素的吸收和利用率较低。②施肥增加了0-10 cm土壤微生物类群PLFAs丰富度尤其细菌和革兰氏阳性菌PLFAs,降低了10-20 cm PLFAs丰富度;③磷脂脂肪酸饱和脂肪酸/单烯不饱和脂肪酸、细菌PLFAs/真菌PLFAs的比值随土壤层次增加而增加;④0-10 cm土层革兰氏阳性菌、真菌PLFAs含量与pH、土壤速效磷、速效氮、土壤有机质显著正相关(P0.05或P0.01);10-20 cm土层,细菌、革兰氏阳性菌、真菌和总PLFAs含量与土壤有机质含量显著正相关(P0.05或P0.01)。表明藏嵩草沼泽化草甸微生物PLFAs含量和丰富度对施肥的响应存在明显的土层梯度效应,土壤微生物PLFAs含量和丰富度主要受表层土壤初始养分含量的影响。     

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。     

Estimating respiration of roots in soil: Interactions with soil CO2, soil temperature and soil water content

Little information is available on the variability of the dynamics of the actual and observed root respiration rate in relation to abiotic factors. In this study, we describe I) interactions between soil CO₂ concentration, temperature, soil water content and root respiration, and II) the effect of short-term fluctuations of these three environmental factors on the relation between actual and observed root respiration rates. We designed an automated, open, gas-exchange system that allows continuous measurements on 12 chambers with intact roots in soil. By using three distinct chamber designs with each a different path for the air flow, we were able to measure root respiration over a 50-fold range of soil CO₂ concentrations (400 to 25000 ppm) and to separate the effect of irrigation on observed vs. actual root respiration rate. All respiration measurements were made on one-year-old citrus seedlings in sterilized sandy soil with minimal organic material.Root respiration was strongly affected by diurnal fluctuations in temperature (Q₁₀ = 2), which agrees well with the literature. In contrast to earlier findings for Douglas-fir (Qi et al., 1994), root respiration rates of citrus were not affected by soil CO₂ concentrations (400 to 25000 ppm CO₂; pH around 6). Soil CO₂ was strongly affected by soil water content but not by respiration measurements, unless the air flow for root respiration measurements was directed through the soil. The latter method of measuring root respiration reduced soil CO₂ concentration to that of incoming air. Irrigation caused a temporary reduction in CO₂ diffusion, decreasing the observed respiration rates obtained by techniques that depended on diffusion. This apparent drop in respiration rate did not occur if the air flow was directed through the soil. Our dynamic data are used to indicate the optimal method of measuring root respiration in soil, in relation to the objectives and limitations of the experimental conditions.     

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。     

Available soil nitrogen in relation to fractions of soil nitrogen and other soil properties

The available N of 27 soils from England and Wales was assessed from the amounts of N taken up over a 6-month period by perennial ryegrass grown in pots under uniform environmental conditions. Relationships between availability and the distribution of soil N amongst various fractions were then examined using multiple regression. The relationship: available soil N (mg kg^–1 dry soil)=(N_min×0.672)+(N_inc×0.840)+(N_mom×0.227)–5.12 was found to account for 91% of the variance in available soil N, where N_min=mineral N, N_inc=N mineralized on incubation and N_mom=N in macro-organic matter. The N mineralized on incubation appeared to be derived largely from sources other than the macro-organic matter because these two fractions were poorly correlated. When availability was expressed in terms of available organic N as % of soil organic N (N_ao) the closest relationship with other soil characteristics was: N_ao=[N_inc×(1.395–0.0347×CN_mom]+[N_mom×0.1416], where CN_mom=CN ratio of the macro-organic matter. This relationship accounted for 81% of the variance in the availability of the soil organic N.The conclusion that the macro-organic matter may contribute substantially to the available N was confirmed by a subsidiary experiment in which the macro-organic fraction was separated from about 20 kg of a grassland soil. The uptake of N by ryegrass was then assessed on two subsamples of this soil, one without the macro-organic matter and the other with this fraction returned: uptake was appreciably increased by the macro-organic matter.     

The porosity of soil aggregates from bulk soil and from soil adhering to roots

Summary Total porosity and pore-size distribution (p.s.d.) were determined in soil aggregates taken in plots planted with maize and treated with farmyard manure and three rates of compost. Soil aggregates were collected from the soil adherent to the maize roots (root soil aggregates) and from bulk soil (bulk soil aggregates). Mercury intrusion porosimetry was used to evaluate the total porosity and the p.s.d. Treatments did not affect the total porosity of the bulk soil aggregates. The same was observed for the root soil aggregates. However the total porosity of the root soil aggregates was always lower than that of the bulk soil aggregates. The loss of total porosity was found to be due to a decrease in the percentage of larger pores with respect to the total.     

Linking soil bacterial biodiversity and soil carbon stability

Native soil carbon (C) can be lost in response to fresh C inputs, a phenomenon observed for decades yet still not understood. Using dual-stable isotope probing, we show that changes in the diversity and composition of two functional bacterial groups occur with this ‘priming'' effect. A single-substrate pulse suppressed native soil C loss and reduced bacterial diversity, whereas repeated substrate pulses stimulated native soil C loss and increased diversity. Increased diversity after repeated C amendments contrasts with resource competition theory, and may be explained by increased predation as evidenced by a decrease in bacterial 16S rRNA gene copies. Our results suggest that biodiversity and composition of the soil microbial community change in concert with its functioning, with consequences for native soil C stability.Substrate inputs can stimulate decomposition of native soil organic carbon (SOC; Kuzyakov et al., 2000), a phenomenon known as the ‘priming effect'' (Kuzyakov, 2010), and is considered large enough to influence ecosystem C balance (Wieder et al., 2013). Two functionally distinct groups of microorganisms are postulated to mediate priming: one that grows rapidly utilizing labile C, and one that grows slowly, breaking down recalcitrant SOC (Fontaine et al., 2003; Blagodatskaya et al., 2007). However, distinguishing these groups is technically challenging. Here, we used dual-stable isotope probing with ¹³C-glucose and ¹⁸O-water to identify bacteria in these two groups growing in response to single and repeated pulses of glucose. Organisms that utilize labile C for growth assimilate both ¹³C-glucose and ¹⁸O-water into their DNA, whereas organisms that grow using SOC incorporate only ¹⁸O-water. Differential isotope incorporation leads to a range of DNA densities separable through isopycnic centrifugation, which can then be characterized by sequencing (Radajewski et al., 2000).We sequenced fragments of bacterial 16S rRNA genes following single and repeated glucose pulses. We hypothesized that the single pulse of labile C would stimulate growth of opportunistic organisms, thus immobilizing nutrients and suppressing growth and diversity of the SOC-utilizing community, decreasing SOC decomposition (negative priming), a response analogous to that observed in plant communities in response to chronic N additions (Tilman, 1987; Clark and Tilman, 2008). We hypothesized that multiple glucose additions would stimulate growth of a more diverse bacterial community, including more native SOC-utilizing organisms that possess enzymes to decompose recalcitrant compounds, causing positive priming (Fontaine et al., 2003; Kuzyakov, 2010).Soil from a ponderosa pine ecosystem was amended weekly for 7 weeks with 500 μg C-glucose per gram soil (2.65 atom % ¹³C) in 100 μl deionized water or with 100 μl deionized water (n=5). Measurements of δ¹³C–CO₂ and [CO₂] enabled the partitioning of CO₂ into that derived from added glucose or from native SOC (C_SOC):where C_total is CO₂–C from glucose-amended samples, δ_total is the δ¹³C–CO₂ from glucose-amended samples, δ_glucose is the δ¹³C of the added glucose and δ_SOC is the δ¹³C–CO₂ evolved from the non-amended samples. Priming was calculated as the difference between SOC oxidation of the amended and non-amended samples. With this approach, any evolved CO₂ carrying the ¹³C signature of the added glucose is considered respiration of glucose, including ¹³C-labeled biomass and metabolites derived from prior glucose additions. Thus, this approach quantifies priming as the oxidation of SOC present at the beginning of the experiment, consistent with many other studies of priming (Cheng et al., 2003; De Graaff et al., 2010).In a parallel incubation for dual-stable isotope probing, the repeated-pulse samples received unlabeled glucose (500 μg C-glucose per gram soil) for 6 weeks while the non-amended and single-pulse samples received sterile deionized water. In week 7, samples received one of four isotope treatments (n=3): 97 atom % H₂ ¹⁸O (non-amended soil), 99 atom % ¹³C-glucose and 97 atom % H₂ ¹⁸O (single- and repeated-pulse soil), ¹²C-glucose and 97 atom % H₂ ¹⁸O (repeated-pulse soil) or ¹²C-glucose and H₂ ¹⁶O (repeated-pulse soil). After incubating for 7 days, soil was frozen at −40 °C. DNA was extracted, separated through isopycnic centrifugation, and two density ranges were sequenced for the bacterial 16S rRNA gene (Supplementary Figure 1): 1.731–1.746 g ml⁻¹ (hereafter called the SOC-utilizing community) and 1.759–1.774 g ml⁻¹ (hereafter called the glucose-utilizing community).Amplicons of the V3–V6 16S rRNA region were bar coded with broad-coverage fusion PCR primers and pooled before sequencing on a Genome Sequencer FLX instrument. These sequence data have been submitted to the GenBank database under accession number SRP043371. Data were checked for chimeras (Edgar et al., 2011), demultiplexed and quality checked (Caporaso et al., 2010). Taxonomy was assigned to genus at the ⩾80% bootstrap confidence level (Cole et al., 2009).We used the Shannon''s diversity index (H′), commonly used in microbial systems (Fierer and Jackson, 2006), to assess changes in microbial diversity. Analysis of variance was used to compare the amount of DNA within densities between isotope treatments (Supplementary Figure 2) and to test the effects of the treatments on the Shannon''s diversity (Figure 2) and Pielou''s evenness (Supplementary Figure 3) of the active bacterial communities, with post hoc Student''s t-tests, α=0.05. PRIMER 6 and PERMANOVA were used to create the nonmetric multidimensional scaling ordination and to compare bacterial communities between glucose treatments and the two sequenced density ranges.The single pulse of glucose suppressed SOC oxidation, whereas repeated pulses increased SOC oxidation (Figure 1). Few experiments to date have examined priming in response to repeated substrate amendments (Hamer and Marschner, 2005; Qiao et al., 2014), even though in nature soil receives repeated substrate pulses from litterfall and rhizodeposition. Our results demonstrate the dynamic response of SOC decomposition to repeated labile C inputs.Open in a separate windowFigure 1Weekly priming rates calculated as the difference in SOC respired between glucose-amended and non-amended soil (n=5).Dual-stable isotope probing was able to separate the growing bacteria into two groups with distinct DNA densities (P<0.001, PERMANOVA; Figure 3a), indicating differential uptake of ¹³C-glucose and ¹⁸O-water. In response to the initial glucose addition, the diversity of the growing glucose- and SOC-utilizing bacterial communities declined compared with the non-amended community (P<0.001, t-tests; Figure 2), driven by a strong decrease in evenness (Supplementary Figure 3). In the SOC-utilizing community, where DNA was labeled with ¹⁸O only, the relative abundance of Bacillus increased 4.9-fold compared with the non-amended control to constitute 31.6% of the community (Figure 3b). Bacillus survives well under low-nutrient conditions (Panikov, 1995), and is able to synthesize a suite of extracellular enzymes capable of degrading complex substrates (Priest, 1977), traits that are conducive for using SOC for growth. In the glucose-utilizing community, where DNA was labeled with both ¹³C and ¹⁸O, Arthrobacter increased 67.7-fold relative to the non-amended control to constitute 75.5% of the growing bacteria (Figure 3b). In culture experiments, Arthrobacter can rapidly take up and store glucose for later use (Panikov, 1995) and here we find it dominating the high-density DNA fractions, signifying that it is using the labeled glucose to grow. The increased biomass of Arthrobacter may have resulted in greater resource competition, thus reducing the diversity of the growing community, as is frequently found in plant communities (Bakelaar and Odum, 1978; Clark and Tilman, 2008).Open in a separate windowFigure 2Shannon''s diversity index (H′) of the non-amended, single-pulse, and repeated-pulse treatments (n=3) in the SOC- (mid-density) and glucose-utilizing (high-density) communities. Treatments with the same letter are not significantly different from each other (Student''s t, α=0.05).Open in a separate windowFigure 3(a) Nonmetric multidimensional scaling ordination showing differences in growing bacterial communities at the genus taxonomic level in the SOC-utilizing (mid-density; open symbols) and glucose-utilizing (high-density; closed symbols) groups of non-amended (Δ), single-pulse (○) and repeated-pulse (□) treatments (n=3). (b) Pie charts of genera in the SOC- and glucose-utilizing communities of the single- and repeated-pulse treatments (n=3). Genera with relative abundances >5% are listed in the figure legend.After repeated glucose amendments, the diversity of the growing community recovered to non-amendment levels (Figure 2) without strongly dominant organisms (Figure 3b and Supplementary Figure 3). The higher diversity found after repeated glucose pulses may be explained by trophic interactions where predators graze on prey populations that have been enlarged by resource addition, suppressing competition between prey species and causing secondary mobilization of nutrients (Clarholm, 1985). The decrease in total bacterial 16S rRNA gene copies in the repeated-pulse—compared with the single-pulse—treatment (Supplementary Figure 4) supports predation as a potential mechanism explaining the observed diversity increase after repeated glucose pulses.The recovery of diversity after repeated glucose pulses contrasts with resource competition theory (Tilman, 1987). When chronic additions of a limiting resource are applied, species diversity and evenness typically decrease (Bakelaar and Odum, 1978; Clark and Tilman, 2008) because competitive organisms become dominant. We observed this after the single glucose pulse, but not after repeated pulses. This diversity response may be the result of community shifts facilitated by short bacterial life cycles and the tens to hundreds of generations expected during the 7-week incubation (Behera and Wagner, 1974). In contrast, systems on which most ecological theory is based (for example, plants) might achieve perhaps 20 generations in a multi-decadal field experiment (Bakelaar and Odum, 1978; Clark and Tilman, 2008). With more generations, more community dynamics can occur, including increased resource cascades in which extracellular enzymes, metabolites or lysed cells of one functional group increase substrates for another (Blagodatskaya and Kuzyakov, 2008). Our results highlight the opportunity to test ecological theories in microbial ecosystems (Prosser et al., 2007), particularly as the short life cycles of microbes makes them well suited for pursuing ecological questions in an evolutionary framework (Jessup et al., 2004).The priming effect is ubiquitous, yet its drivers remain elusive. Our results suggest that changes in the diversity and composition of the growing bacterial community contribute to priming, and thus that ecosystem properties such as soil C storage may be sensitive to soil microbial biodiversity.     

耕作方式对潮土土壤团聚体微生物群落结构的影响

为探究不同耕作方式对潮土土壤团聚体微生物群落结构和多样性的影响,采用磷脂脂肪酸(PLFA)法测定了土壤团聚体中微生物群落。试验设置4个耕作处理,分别为旋耕+秸秆还田(RT)、深耕+秸秆还田(DP)、深松+秸秆还田(SS)和免耕+秸秆还田(NT)。结果表明:与RT相比,DP处理显著提高了原状土壤和>5 mm粒级土壤团聚体中真菌PLFAs量和真菌/细菌,为真菌的繁殖提供了有利条件,有助于土壤有机质的贮存,提高了土壤生态系统的缓冲能力;提高了5～2 mm粒级土壤团聚体中细菌PLFAs量,降低了土壤革兰氏阳性菌/革兰氏阴性菌,改善了土壤营养状况;提高了<0.25 mm粒级土壤团聚体中微生物丰富度指数。总的来说,深耕+秸秆还田(DP)对土壤团聚体细菌和真菌生物量有一定的提高作用,并且在一定程度上改善了土壤团聚体微生物群落结构,有利于增加土壤固碳能力和保持土壤微生物多样性。冗余分析结果表明,土壤团聚体总PLFAs量、细菌、革兰氏阴性菌和放线菌PLFAs量与土壤有机碳相关性较强,革兰氏阳性菌PLFAs量与总氮相关性较强。各处理较大粒级土壤团聚体微生物群落主要受碳氮比、含水量、pH值和团聚体质量分数的影响,较小粒级土壤团聚体微生物群落则主要受土壤有机碳和总氮的影响。     

酸性硫酸盐土水改旱后土壤化学性状的变异初报

探讨了酸性硫酸盐水稻土改为旱作后土壤化学性状的变异以及比较不同利用方式之间的经济效益．结果表明,酸性硫酸盐水稻土改种甜玉米和蔬菜后,土壤化学性状发生显著变化．耕层土壤酸度、水溶性硫酸根含量、土壤活性铝和活性铁含量均显著降低．经济效益得到显著提高．建议对水改旱后的环境效应进行深入研究以及进行定位观测,以便合理利用这一特殊的土壤资源     

Carbon input to soil may decrease soil carbon content

It is commonly predicted that the intensity of primary production and soil carbon (C) content are positively linked. Paradoxically, many long‐term field observations show that although plant litter is incorporated to soil in large quantities, soil C content does not necessarily increase. These results suggest that a negative relationship between C input and soil C conservation exists. Here, we demonstrate in controlled conditions that the supply of fresh C may accelerate the decomposition of soil C and induce a negative C balance. We show that soil C losses increase when soil microbes are nutrient limited. Results highlight the need for a better understanding of microbial mechanisms involved in the complex relationship between C input and soil C sequestration. We conclude that energy available to soil microbes and microbial competition are important determinants of soil C decomposition.