根系去除改变了毛竹林土壤酶活性对氮磷添加的响应

亚热带是我国氮和磷沉降的热点地区,森林生态系统碳（C）、氮（N）、磷（P）循环对N和P沉降的响应受到广泛关注。根系作为森林土壤碳和养分持续供给的重要来源,其输入变化在N和P沉降下通过影响土壤酶活性进而调控土壤碳和养分循环过程。以毛竹林为研究对象,选择硝酸铵和磷酸二氢钠分别进行N和P添加,共设置4个处理：对照、N添加、P添加和N+P添加,并结合壕沟处理,探究毛竹林土壤C、N、P循环相关酶活性对氮磷添加和根系去除的响应,并分析它们与土壤和细根化学性质之间的关系。结果表明：土壤C、N循环相关酶活性整体上对根系去除的响应比氮磷添加更敏感,这主要是因为根系去除显著降低土壤全氮和铵态氮含量,但短期氮磷添加并未显著改变调控土壤酶活性分异的土壤有机碳、全氮和铵态氮含量。与C、N循环相关酶活性不同,土壤P循环相关酶对根系去除和磷添加处理均呈现负响应,这可能是因为阻断根系P吸收和补充土壤P元素降低了微生物的P开采作用。但研究区土壤微生物仍受到P限制作用,这是因为在P缺乏毛竹林生态系统,根系比微生物具有更强的P吸收利用能力。研究结果强调了不同功能土壤酶活性对土壤养分添加和根系输入变化响应的敏感性差异,为预测低P毛竹林生态系统土壤C和养分循环提供依据。     

高寒草甸植物化学计量比对磷添加的分层响应

为了探明氮(N)限制的植物群落中物种水平和功能群水平的碳(C)、N、磷(P)含量以及C:N:P对P添加的响应是否一致,明确P添加对群落物种构成改变的内在机制。以青藏高原高寒草甸为研究对象, 通过P添加试验, 研究了功能群水平和物种水平生态化学计量比对P添加的响应, 以及P添加对物种水平的优势度和功能群水平生物量的影响。结果表明: 在青藏高原高寒草甸连续5年添加P显著改变了植物的C、N、P含量以及C:N:P, 且在物种水平和功能群水平(不含典型物种)的响应规律基本一致。在禾本科、莎草科和杂类草功能群(不含典型物种)和相应物种水平上P添加对C含量影响不显著。P添加显著增加了禾本科、莎草科、豆科和杂类草4个功能群(不含典型物种)和相应物种水平的植物P含量, 降低了C:P和N:P。禾本科和莎草科的N含量和C:N对P添加在物种水平和功能群水平上(不含典型物种)的响应规律一致, 表现为N含量显著降低, C:N显著增加; P添加使豆科物种水平上N含量显著增加而C:N显著降低, 但在功能群水平上(不含典型物种)无显著作用; 杂类草的N含量和C:N对P添加在物种水平和功能群水平上(不含典型物种)的响应规律均不一致。在N限制的生境中添加P, 禾本科物种在群落中逐渐占据优势跟其增高的N、P利用效率相关, 而杂类草由于逐渐降低的N和P利用效率使其生物量在群落中所占的比重逐渐下降。     

Hierarchical responses of plant stoichiometry to phosphorus addition in an alpine meadow community

为了探明氮(N)限制的植物群落中物种水平和功能群水平的碳(C)、N、磷(P)含量以及C:N:P对P添加的响应是否一致,明确P添加对群落物种构成改变的内在机制。以青藏高原高寒草甸为研究对象, 通过P添加试验, 研究了功能群水平和物种水平生态化学计量比对P添加的响应, 以及P添加对物种水平的优势度和功能群水平生物量的影响。结果表明: 在青藏高原高寒草甸连续5年添加P显著改变了植物的C、N、P含量以及C:N:P, 且在物种水平和功能群水平(不含典型物种)的响应规律基本一致。在禾本科、莎草科和杂类草功能群(不含典型物种)和相应物种水平上P添加对C含量影响不显著。P添加显著增加了禾本科、莎草科、豆科和杂类草4个功能群(不含典型物种)和相应物种水平的植物P含量, 降低了C:P和N:P。禾本科和莎草科的N含量和C:N对P添加在物种水平和功能群水平上(不含典型物种)的响应规律一致, 表现为N含量显著降低, C:N显著增加; P添加使豆科物种水平上N含量显著增加而C:N显著降低, 但在功能群水平上(不含典型物种)无显著作用; 杂类草的N含量和C:N对P添加在物种水平和功能群水平上(不含典型物种)的响应规律均不一致。在N限制的生境中添加P, 禾本科物种在群落中逐渐占据优势跟其增高的N、P利用效率相关, 而杂类草由于逐渐降低的N和P利用效率使其生物量在群落中所占的比重逐渐下降。     

氮沉降对内蒙古典型草原地表节肢动物的影响

了解氮沉降增加背景下草原生态系统结构和功能的响应特征,是研发草原可持续管理措施的基础。目前内蒙古典型草原有关氮沉降增加的研究主要集中在植物群落,而对土壤动物影响的研究较少。通过在内蒙古典型草原连续5年的养分添加实验,研究了地表节肢动物对不同氮添加(N_0、N_(2.5)、N_5、N_(10))处理的响应,并分析了4种氮添加处理下地表节肢动物与环境因子之间的关系。结果表明,氮输入增加后,地表节肢动物群落的多样性并没有显著降低(P0.05),群落多度也没有显著增加(P0.05),仅在低氮处理下,群落生物量显著高于对照(P0.05)。不同地表节肢动物功能群对各水平N添加的响应均不太敏感,捕食性、杂食性、腐食性功能群动物的生物量对N添加都没有显著响应(P0.05),仅植食性动物的生物量在低氮和高氮处理显著高于对照(P0.05)。回归分析表明,植食性节肢动物的多度和生物量主要受植物叶氮含量显著影响(P0.05),而腐食性节肢动物的多度、生物量和类群数受土壤有机碳显著影响(P0.05)。研究表明,温带典型草原地表节肢动物对氮添加的响应受其食物来源影响,明显滞后于植物群落;不同功能群对氮添加有不同响应形式,是群落水平响应较弱的主要原因。     

氮添加对武夷山亚热带常绿阔叶林植物叶片氮磷化学计量特征的影响

该文以福建武夷山亚热带常绿阔叶林为研究对象, 通过设置3个氮(N)添加梯度的野外实验, 研究了群落内乔木植物、灌木植物、草本植物、蕨类植物和苔藓植物叶片N、磷(P)化学计量特征对N沉降的响应, 以及不同功能群和物种化学计量特征对N沉降响应的差异。在已开展5年人工N添加的样地内, 3年的监测结果表明: N添加整体上提高了植物叶片N含量, 草本层植物叶片N含量对N添加的响应比乔木层和灌木层植物更加敏感, 优势种米槠(Castanopsis carlesii)、草本植物砂仁(Amomum villosum)、蕨类植物狗脊(Woodwardia japonica)的叶片N含量显著增加。N添加整体上增加了植物叶片P含量, 乔木层植物和灌木层植物叶片P含量没有显著变化, 草本层植物叶片P含量显著增加, 而苔藓植物叶片P含量显著减少。N添加促使武夷山亚热带常绿阔叶林植物叶片N:P由18.67上升至19.72, 加剧了植物生长的P限制; 乔木物种N:P的变化较灌木和草本物种更加稳定。N添加条件下, 植物叶片N:P的变化主要受到叶片P含量而非N含量变化的影响, N添加对生态系统P循环的影响显著。     

氮添加诱导的磷限制改变了亚热带黄山松林土壤微生物群落结构

土壤微生物在陆地生态系统的生物地球化学循环中起着重要作用。然而目前尚不清楚氮(N)添加量及其持续时间如何影响土壤微生物群落结构,以及微生物群落结构变化与微生物相对养分限制状况是否存在关联。本研究在亚热带黄山松林开展了N添加试验以模拟N沉降,并设置3个处理:对照(CK, 0 kg N·hm^-2·a^-1)、低N(LN, 40 kg N·hm^-2·a^-1)和高N(HN, 80 kg N·hm^-2·a^-1)。在N添加满1年和3年时测定土壤基本理化性质、磷脂脂肪酸含量和碳(C)、N、磷(P)获取酶活性,并通过生态酶化学计量分析土壤微生物的相对养分限制状况。结果表明: 1年N添加对土壤微生物群落结构无显著影响,3年LN处理显著提高了革兰氏阳性菌(G⁺)、革兰氏阴性菌(G^-)、放线菌(ACT)和总磷脂脂肪酸(TPLFA)含量,而3年HN处理对微生物的影响不显著,表明细菌和ACT对N添加可能更为敏感。N添加加剧了微生物C和P限制,而P限制是土壤微生物群落结构变化的最佳解释因子。这表明,N添加诱导的P限制可能更有利于部分贫营养菌(如G⁺)和参与P循环的微生物(如ACT)的生长,从而改变亚热带黄山松林土壤微生物群落结构。     

羊草的地上-地下功能性状对氮磷施肥梯度的响应及关联

羊草(Leymus chinensis)是我国北方典型草原群落的主要建群种和优势种, 由于长期的过度放牧, 羊草草原生态系统的结构和功能严重退化。养分添加作为恢复草地生态系统的一种管理措施, 其应用目前还处于实验性研究阶段。关于羊草的地上-地下功能性状对养分添加, 尤其是P添加的响应研究较少, 相关机制尚不十分清楚。为此, 该文以羊草为研究对象, 通过温室栽培进行N (50, 100, 250 mg N·kg^-1)和P (5, 10, 25 mg P·kg^-1)各3个水平的养分添加实验, 研究羊草的地上-地下功能性状对N、P添加的响应及适应机制。主要研究结果表明: 1)羊草的地上生物量和总生物量主要受N添加的影响, N添加显著提高了羊草的地上生物量, 而地下生物量主要受P添加的影响, 尤其在中N和高N水平, P添加显著降低了羊草的地下生物量。羊草的根冠比受N、P添加的共同影响, 随着N、P添加梯度加大, 根冠比显著降低, N、P添加促进了羊草生物量向地上部分的分配和N、P向叶片的分配。2)在低N和高N水平, 羊草对P添加的响应与适应机制不同。低N水平, 羊草主要通过增加光合速率和比根长(SRL), 提高光合能力和根系对N的获取能力促进地上部分的生长, 而根系对P的吸收有利于地下部分的生长; 在高N水平, P添加对羊草的个体生长无明显促进作用, 甚至地下生物量明显受到P素抑制, 羊草主要通过保持较高的比叶面积(SLA)和SRL, 提高对光资源的截获能力和根系对N的获取和吸收能力, 维持地上部分的生长。3)相对于地上性状, P添加对羊草的地下性状影响更大, 羊草的SLA与SRL呈较弱的正相关关系, 表明叶片与根系在资源获取和利用方面具有相对独立性。     

典型草原建群种羊草对氮磷添加的生理生态响应

由于人类活动和气候变化的共同作用, 大气氮(N)沉降日益加剧, 使得陆地生态系统中的可利用性N显著增加, 生态系统更易受其他元素如磷(P)的限制。然而, 目前关于N、P养分添加对草原生态系统不同组织水平的影响研究较少, 相关机制尚不清楚。该文以内蒙古典型羊草(Leymus chinensis)草原为研究对象, 通过连续两年(2011-2012年)的N和P养分添加实验, 研究建群种羊草的生理生态性状、种群生物量和群落初级生产力对N、P添加的响应及其适应机制。结果表明: 羊草草原不同组织水平对N、P添加的响应不同。群落水平上, 地上净初级生产力在不同降水年份均受N和P元素的共同限制, N、P共同添加显著提高了地上净初级生产力; 物种水平上, N、P添加对羊草种群生物量和密度, 以及相对生物量均没有显著影响, 表明羊草能够维持种群的相对稳定; 个体水平上, 在正常降水年份(2011年), 羊草生长主要受N素限制, 而在湿润年份(2012年), 降水增加使得羊草生长没有受到明显的养分限制。羊草通过增加比叶面积、叶片大小和叶片N含量, 提高整体光合能力, 以促进个体生长。总之, 内蒙古典型草原群落净初级生产力受N、P元素共同限制, 作为建群种的羊草, 其对N、P添加的响应因组织水平而异, 也受年际间降水变化的影响。     

青藏高原高寒草甸植物群落生物量对氮、磷添加的响应

青藏高原正经历着明显的温暖化过程, 由此引起的土壤温度的升高促进了土壤中微生物的活性, 同时青藏高原东缘地区大气氮沉降十分明显, 并呈逐年增加的趋势, 这些环境变化均促使土壤中可利用营养元素增加, 因此深入了解青藏高原高寒草甸植物生物量对可利用营养元素增加的响应, 是准确预测未来全球变化背景下青藏高原高寒草甸碳循环过程的重要基础。该研究基于在青藏高原高寒草甸连续4年(2009-2012年)氮、磷添加后对不同功能群植物地上生物量、群落地上和地下生物量的测定, 探讨高寒草甸生态系统碳输入对氮、磷添加的响应。结果表明: (1)氮、磷添加均极显著增加了禾草的地上绝对生物量及其在群落总生物量中所占的比例, 同时均显著降低了杂类草在群落总生物量中的比例, 此外磷添加极显著降低了莎草地上绝对生物量及其在群落总生物量中所占的比例。(2)氮、磷添加均显著促进了青藏高原高寒草甸的地上生物量增加, 分别增加了24%和52%。(3)氮添加对高寒草甸地下生物量无显著影响, 而磷添加后地下生物量有增加的趋势。(4)氮添加对高寒草甸植物总生物量无显著影响, 而磷添加后植物总生物量显著增加。研究表明, 氮、磷添加可缓解青藏高原高寒草甸植物生长的营养限制, 促进植物地上部分的生长, 然而高寒草甸植物的生长极有可能更受土壤中可利用磷含量的限制。     

环青海湖地区天然草地和退耕恢复草地植物群落生物量对氮、磷添加的响应

植物群落生物量反映了植被的初级生产能力, 是陆地生态系统碳(C)输入的最主要来源, 往往受到自然界中氮(N)、磷(P)元素供应的限制。该试验以青藏高原环青海湖地区的高寒草原为研究对象, 探讨了天然草地和退耕恢复草地植被群落生物量对N (10 g·m^-2)、P (5 g·m^-2)养分添加的响应。N、P添加显著增加了天然草地禾草的生物量, 进而促使地上总生物量显著提高。退耕恢复草地禾草和杂类草的生物量对N添加均有一致的正响应, 从而促使地上总生物量显著增加174%, 群落地上和地下总生物量显著增加34%; 而P添加对恢复草地生物量各项参数均无显著影响。回归分析显示: 天然草地植物群落地上生物量随土壤中NO₃^--N含量的增加而增加(p < 0.05), 退耕恢复草地植被地上、地下和总生物量均与土壤NO₃^--N含量显著正相关(p < 0.01), 说明环湖地区高寒草原植物生长主要受N供应的限制, P的限制作用随土地利用方式的转变和群落演替阶段的不同而变化; 相比天然草地, 恢复草地在现阶段植被初级生产力受N的限制作用更强烈, 土壤中可利用N含量是限制其植被自然恢复和重建的关键因子。     

半干旱黄土区不同管理措施下草地群落结构对短期氮、水添加的响应

氮沉降和降水变异显著影响草地群落结构和功能,但缺乏对不同管理措施下草地群落结构对氮沉降和降水变异响应的研究。为模拟不同管理措施下草地群落结构对氮沉降和降水变异的响应特征,以半干旱黄土区云雾山国家自然保护区典型草原为研究对象,系统分析了在封育、刈割和火烧三种管理措施下,氮添加和水添加对群落地上生物量、功能群组成和群落多样性的影响。结果表明,氮添加和水添加对地上生物量、功能群组成和群落多样性指数的影响因管理措施不同有所差异。（1）在封育草地上,氮添加显著降低物种多样性,对地上生物量影响较小;水添加显著增加物种多样性指数,氮添加和水添加的交互作用显著增加地上生物量、禾本科所占比例和莎草科所占比例;物种多样性指数均与地上生物量无显著相关,与不同功能群所占比例显著相关。（2）在刈割草地上,氮添加和水添加显著提高草地群落地上生物量,氮添加和水添加交互作用尤为显著;氮添加和水添加显著增加物种丰富度指数,对物种均匀度影响较小;杂草类所占比例和地上生物量对Shannon-Weiner多样性指数的贡献率较大。（3）在火烧草地上,氮添加和水添加显著提高群落地上生物量,对物种多样性的影响因年份不同有所差异,氮添加和水添加交互作用具有累加效应;Shannon-Weiner多样性指数与地上生物量呈显著负相关,与莎草科所占比例呈显著正相关。研究表明管理措施显著影响群落结构对氮添加和水添加的响应特征,亦改变生产力和物种多样性的关系模式,为更好地应对全球变化进行草地管理提供数据支撑。     

Impact of nitrogen deposition on forest and lake food webs in nitrogen‐limited environments

Increased reactive nitrogen (N_r) deposition has raised the amount of N available to organisms and has greatly altered the transfer of energy through food webs, with major consequences for trophic dynamics. The aim of this review was to: (i) clarify the direct and indirect effects of N_r deposition on forest and lake food webs in N‐limited biomes, (ii) compare and contrast how aquatic and terrestrial systems respond to increased N_r deposition, and (iii) identify how the nutrient pathways within and between ecosystems change in response to N_r deposition. We present that N_r deposition releases primary producers from N limitation in both forest and lake ecosystems and raises plants' N content which in turn benefits herbivores with high N requirements. Such trophic effects are coupled with a general decrease in biodiversity caused by different N‐use efficiencies; slow‐growing species with low rates of N turnover are replaced by fast‐growing species with high rates of N turnover. In contrast, N_r deposition diminishes below‐ground production in forests, due to a range of mechanisms that reduce microbial biomass, and decreases lake benthic productivity by switching herbivore growth from N to phosphorus (P) limitation, and by intensifying P limitation of benthic fish. The flow of nutrients between ecosystems is expected to change with increasing N_r deposition. Due to higher litter production and more intense precipitation, more terrestrial matter will enter lakes. This will benefit bacteria and will in turn boost the microbial food web. Additionally, N_r deposition promotes emergent insects, which subsidize the terrestrial food web as prey for insectivores or by dying and decomposing on land. So far, most studies have examined N_r‐deposition effects on the food web base, whereas our review highlights that changes at the base of food webs substantially impact higher trophic levels and therefore food web structure and functioning.     

夏季若尔盖高寒湿地水生生物群落食物网结构特征

为了解若尔盖高寒湿地夏季水生生物群落食物网结构及营养关系特征,应用稳定同位素技术分析了若尔盖湿地 3个不同区域(ZS1、ZS2和ZS3)水生生物群落碳、氮稳定同位素比值,并计算了13C-15N同位素生态位中的6个营养结构量化指标。结果显示:外源性营养源陆生植物13C、15N值分别为-28.23- -26.07,-1.20-5.98; 内源性营养源颗粒有机物 (POM:主要成分为藻类)和水生植物13C、15N值分别为-26.39- -21.17、-25.37- -24.15,3.68-6.61、3.50-4.01; 其中POM样品13C、15N组成存在明显的区域性差异(P0.05,P0.001)。食物网营养结构分析显示若尔盖湿地外源性碳源输入(优势陆生植物)对于维持该水域生态系统结构稳定有着十分重要的作用。若尔盖湿地水域食物网营养级介于2-3,暗示了其生态系统结构的相对脆弱性。同位素量化指标标记发现若尔盖湿地水生动物群落生态结构存在明显的空间异质性,可能与若尔盖湿地发达的畜牧产业相关。     

Intraguild interactions between spiders and ants and top-down control in a grassland food web

In most terrestrial ecosystems ants (Formicidae) as eusocial insects and spiders (Araneida) as solitary trappers and hunters are key predators. To study the role of predation by these generalist predators in a dry grassland, we manipulated densities of ants and spiders (natural and low density) in a two-factorial field experiment using fenced plots. The experiment revealed strong intraguild interactions between ants and spiders. Higher densities of ants negatively affected the abundance and biomass of web-building spiders. The density of Linyphiidae was threefold higher in plots without ant colonies. The abundance of Formica cunicularia workers was significantly higher in spider-removal plots. Also, population size of springtails (Collembola) was negatively affected by the presence of wandering spiders. Ants reduced the density of Lepidoptera larvae. In contrast, the abundance of coccids (Ortheziidae) was positively correlated with densities of ants. To gain a better understanding of the position of spiders, ants and other dominant invertebrate groups in the studied food web and important trophic links, we used a stable isotope analysis (¹⁵N and ¹³C). Adult wandering spiders were more enriched in ¹⁵N relative to ¹⁴N than juveniles, indicating a shift to predatory prey groups. Juvenile wandering and web-building spiders showed δ¹⁵N ratios just one trophic level above those of Collembola, and they had similar δ¹³C values, indicating that Collembola are an important prey group for ground living spiders. The effects of spiders demonstrated in the field experiment support this result. We conclude that the food resource of spiders in our study system is largely based on the detrital food web and that their effects on herbivores are weak. The effects of ants are not clear-cut and include predation as well as mutualism with herbivores. Within this diverse predator guild, intraguild interactions are important structuring forces.     

Drought decreases incorporation of recent plant photosynthate into soil food webs regardless of their trophic complexity

Theory suggests that more complex food webs promote stability and can buffer the effects of perturbations, such as drought, on soil organisms and ecosystem functions. Here, we tested experimentally how soil food web trophic complexity modulates the response to drought of soil functions related to carbon cycling and the capture and transfer below‐ground of recent photosynthate by plants. We constructed experimental systems comprising soil communities with one, two or three trophic levels (microorganisms, detritivores and predators) and subjected them to drought. We investigated how food web trophic complexity in interaction with drought influenced litter decomposition, soil CO₂ efflux, mycorrhizal colonization, fungal production, microbial communities and soil fauna biomass. Plants were pulse‐labelled after the drought with ¹³C‐CO₂ to quantify the capture of recent photosynthate and its transfer below‐ground. Overall, our results show that drought and soil food web trophic complexity do not interact to affect soil functions and microbial community composition, but act independently, with an overall stronger effect of drought. After drought, the net uptake of ¹³C by plants was reduced and its retention in plant biomass was greater, leading to a strong decrease in carbon transfer below‐ground. Although food web trophic complexity influenced the biomass of Collembola and fungal hyphal length, ¹³C enrichment and the net transfer of carbon from plant shoots to microbes and soil CO₂ efflux were not affected significantly by varying the number of trophic groups. Our results indicate that drought has a strong effect on above‐ground–below‐ground linkages by reducing the flow of recent photosynthate. Our results emphasize the sensitivity of the critical pathway of recent photosynthate transfer from plants to soil organisms to a drought perturbation, and show that these effects may not be mitigated by the trophic complexity of soil communities, at least at the level manipulated in this experiment.     

Legacy effects of drought on plant growth and the soil food web

Soils deliver important ecosystem services, such as nutrient provision for plants and the storage of carbon (C) and nitrogen (N), which are greatly impacted by drought. Both plants and soil biota affect soil C and N availability, which might in turn affect their response to drought, offering the potential to feed back on each other’s performance. In a greenhouse experiment, we compared legacy effects of repeated drought on plant growth and the soil food web in two contrasting land-use systems: extensively managed grassland, rich in C and with a fungal-based food web, and intensively managed wheat lower in C and with a bacterial-based food web. Moreover, we assessed the effect of plant presence on the recovery of the soil food web after drought. Drought legacy effects increased plant growth in both systems, and a plant strongly reduced N leaching. Fungi, bacteria, and their predators were more resilient after drought in the grassland soil than in the wheat soil. The presence of a plant strongly affected the composition of the soil food web, and alleviated the effects of drought for most trophic groups, regardless of the system. This effect was stronger for the bottom trophic levels, whose resilience was positively correlated to soil available C. Our results show that plant belowground inputs have the potential to affect the recovery of belowground communities after drought, with implications for the functions they perform, such as C and N cycling.     

Divergence of feeding channels within the soil food web determined by ecosystem type

Understanding trophic linkages within the soil food web (SFW) is hampered by its opacity, diversity, and limited niche adaptation. We need to expand our insight between the feeding guilds of fauna and not just count biodiversity. The soil fauna drive nutrient cycling and play a pivotal, but little understood role within both the carbon (C) and nitrogen (N) cycles that may be ecosystem dependent. Here, we define the structure of the SFW in two habitats (grassland and woodland) on the same soil type and test the hypothesis that land management would alter the SFW in these habitats. To do this, we census the community structure and use stable isotope analysis to establish the pathway of C and N through each trophic level within the ecosystems. Stable isotope ratios of C and N from all invertebrates were used as a proxy for trophic niche, and community‐wide metrics were obtained. Our empirically derived C/N ratios differed from those previously reported, diverging from model predictions of global C and N cycling, which was unexpected. An assessment of the relative response of the different functional groups to the change from agricultural grassland to woodland was performed. This showed that abundance of herbivores, microbivores, and micropredators were stimulated, while omnivores and macropredators were inhibited in the grassland. Differences between stable isotope ratios and community‐wide metrics, highlighted habitats with similar taxa had different SFWs, using different basal resources, either driven by root or litter derived resources. Overall, we conclude that plant type can act as a top‐down driver of community functioning and that differing land management can impact on the whole SFW.     

Uncovering trophic positions and food resources of soil animals using bulk natural stable isotope composition

Despite the major importance of soil biota in nutrient and energy fluxes, interactions in soil food webs are poorly understood. Here we provide an overview of recent advances in uncovering the trophic structure of soil food webs using natural variations in stable isotope ratios. We discuss approaches of application, normalization and interpretation of stable isotope ratios along with methodological pitfalls. Analysis of published data from temperate forest ecosystems is used to outline emerging concepts and perspectives in soil food web research. In contrast to aboveground and aquatic food webs, trophic fractionation at the basal level of detrital food webs is large for carbon and small for nitrogen stable isotopes. Virtually all soil animals are enriched in ¹³C as compared to plant litter. This ‘detrital shift’ likely reflects preferential uptake of ¹³C‐enriched microbial biomass and underlines the importance of microorganisms, in contrast to dead plant material, as a major food resource for the soil animal community. Soil organic matter is enriched in ¹⁵N and ¹³C relative to leaf litter. Decomposers inhabiting mineral soil layers therefore might be enriched in ¹⁵N resulting in overlap in isotope ratios between soil‐dwelling detritivores and litter‐dwelling predators. By contrast, ¹³C content varies little between detritivores in upper litter and in mineral soil, suggesting that they rely on similar basal resources, i.e. little decomposed organic matter. Comparing vertical isotope gradients in animals and in basal resources can be a valuable tool to assess trophic interactions and dynamics of organic matter in soil. As indicated by stable isotope composition, direct feeding on living plant material as well as on mycorrhizal fungi is likely rare among soil invertebrates. Plant carbon is taken up predominantly by saprotrophic microorganisms and channelled to higher trophic levels of the soil food web. However, feeding on photoautotrophic microorganisms and non‐vascular plants may play an important role in fuelling soil food webs. The trophic niche of most high‐rank animal taxa spans at least two trophic levels, implying the use of a wide range of resources. Therefore, to identify trophic species and links in food webs, low‐rank taxonomic identification is required. Despite overlap in feeding strategies, stable isotope composition of the high‐rank taxonomic groups reflects differences in trophic level and in the use of basal resources. Different taxonomic groups of predators and decomposers are likely linked to different pools of organic matter in soil, suggesting different functional roles and indicating that trophic niches in soil animal communities are phylogenetically structured. During last two decades studies using stable isotope analysis have elucidated the trophic structure of soil communities, clarified basal food resources of the soil food web and revealed links between above‐ and belowground ecosystem compartments. Extending the use of stable isotope analysis to a wider range of soil‐dwelling organisms, including microfauna, and a larger array of ecosystems provides the perspective of a comprehensive understanding of the structure and functioning of soil food webs.     

Nitrogen Addition and Warming Independently Influence the Belowground Micro-Food Web in a Temperate Steppe

Climate warming and atmospheric nitrogen (N) deposition are known to influence ecosystem structure and functioning. However, our understanding of the interactive effect of these global changes on ecosystem functioning is relatively limited, especially when it concerns the responses of soils and soil organisms. We conducted a field experiment to study the interactive effects of warming and N addition on soil food web. The experiment was established in 2006 in a temperate steppe in northern China. After three to four years (2009–2010), we found that N addition positively affected microbial biomass and negatively influenced trophic group and ecological indices of soil nematodes. However, the warming effects were less obvious, only fungal PLFA showed a decreasing trend under warming. Interestingly, the influence of N addition did not depend on warming.Structural equation modeling analysis suggested that the direct pathway between N addition and soil food web components were more important than the indirect connections through alterations in soil abiotic characters or plant growth. Nitrogen enrichment also affected the soil nematode community indirectly through changes in soil pH and PLFA. We conclude that experimental warming influenced soil food web components of the temperate steppe less than N addition, and there was little influence of warming on N addition effects under these experimental conditions.