
生物多样性 ›› 2026, Vol. 34 ›› Issue (6): 25441. DOI: 10.17520/biods.2025441 cstr: 32101.14.biods.2025441
胡莎莎1,2, 李志鹏2,*(
)(
), 张卫信4(
), 姚海凤2,3(
), 马磊4, 张晓5(
), 刘晓静6, 龚鑫2(
), 孙新1,2(
), 傅声雷4,*(
)(
)
收稿日期:2025-11-05
接受日期:2026-04-22
出版日期:2026-06-20
发布日期:2026-07-30
通讯作者:
*共同通讯作者 E-mail: zpli@iue.ac.cn; fsl@vip.henu.edu.cn
基金资助:
Shasha Hu1,2, Zhipeng Li2,*(
)(
), Weixin Zhang4(
), Haifeng Yao2,3(
), Lei Ma4, Xiao Zhang5(
), Xiaojing Liu6, Xin Gong2(
), Xin Sun1,2(
), Shenglei Fu4,*(
)(
)
Received:2025-11-05
Accepted:2026-04-22
Online:2026-06-20
Published:2026-07-30
Contact:
*Co-authors for correspondence. E-mail: zpli@iue.ac.cn; fsl@vip.henu.edu.cn
Supported by:摘要: 植物光合产物主要以地上凋落物和根系输入的形式进入土壤, 为地下食物网提供物质与能量。原生生物作为土壤生物多样性的核心组分, 在微生物调控方面发挥重要作用。然而, 凋落物与根系输入对土壤原生生物多样性与群落结构的影响及机制并不清楚。本研究基于宝天曼森林生态系统国家野外科学观测研究站连续6.5年的资源控制实验(移除凋落物与灌木和阻断乔木根系), 应用环境DNA宏条形码技术分析了食细菌者、食真核生物者、杂食者和食碎屑者4类原生生物功能群对植物资源变化的响应。结果表明, 不同原生生物功能群对植物资源变化的响应存在显著差异。总体上, 移除凋落物显著降低了各原生生物功能群的丰富度, 其降幅约为33.7%–47.7% (P < 0.05)。移除凋落物通过降低细菌和真菌丰富度对各原生生物功能类群丰富度产生“自下而上”的影响, 其中, 食细菌者与食真核生物者主要与细菌丰富度下降有关, 食碎屑者与真菌丰富度下降有关, 而杂食者类群则受到细菌和真菌丰富度下降的共同驱动。阻断根系的作用相对较弱, 且阻断灌木根系和乔木根系的效应在不同原生生物功能类群中存在明显差异。阻断乔木根系降低了多个类群的丰富度, 并通过增加土壤含水量间接提高了食真核生物者和食碎屑者丰富度。总体而言, 凋落物与根系资源通过不同路径共同调控土壤原生生物丰富度, 不同原生生物功能类群对两类植物资源的差异化响应, 与其受到土壤性质与微生物资源的差异化调控密切相关。本研究通过揭示原生生物对植物资源输入的响应差异模式, 强调原生生物在连接地上–地下过程、维持土壤微食物网稳定性中的关键作用, 为深入理解土壤生态系统中原生生物的功能机制提供依据。
胡莎莎, 李志鹏, 张卫信, 姚海凤, 马磊, 张晓, 刘晓静, 龚鑫, 孙新, 傅声雷 (2026) 暖温带森林土壤原生生物功能类群对凋落物与根系资源变化的差异性响应. 生物多样性, 34, 25441. DOI: 10.17520/biods.2025441.
Shasha Hu, Zhipeng Li, Weixin Zhang, Haifeng Yao, Lei Ma, Xiao Zhang, Xiaojing Liu, Xin Gong, Xin Sun, Shenglei Fu (2026) Divergent responses of protist functional groups to litter and root resource changes in a warm-temperate forest. Biodiversity Science, 34, 25441. DOI: 10.17520/biods.2025441.
| 土壤理化性质及微生物资源丰富度 Soil properties and microbial resources richness | 移除凋落物 Litter removal (df = 1) | 阻断根系 Root deprivation (df = 2) | 交互作用 Interaction (df = 2) | |||
|---|---|---|---|---|---|---|
| F | P | F | P | F | P | |
| 含水率 Moisture content (%) | 3.42 | 0.08 | 4.42 | < 0.05 | 0.68 | 0.52 |
| 酸碱度 pH | 0.22 | 0.65 | 0.58 | 0.57 | 2.37 | 0.12 |
| 总碳 TC (g/kg) | 6.29 | < 0.05 | 1.88 | 0.18 | 1.75 | 0.20 |
| 总氮 TN (g/kg) | 21.00 | < 0.001 | 2.51 | 0.11 | 1.85 | 0.18 |
| 总磷 TP (g/kg) | 5.76 | < 0.05 | 0.47 | 0.63 | 0.17 | 0.84 |
| 总硫 TS (g/kg) | 4.72 | < 0.05 | 0.0001 | 0.10 | 0.31 | 0.74 |
| 真菌丰富度 Fungal richness | 20.22 | < 0.001 | 2.74 | 0.09 | 0.55 | 0.59 |
| 细菌丰富度 Bacterial richness | 27.75 | < 0.001 | 3.55 | 0.05 | 3.76 | < 0.05 |
表1 基于双因素方差分析(ANOVA)的移除凋落物和阻断根系对土壤理化性质和微生物资源丰富度的影响。加粗字体代表差异显著(P < 0.05)。
Table 1 Effects of litter removal and root deprivation on soil physicochemical properties and microbial resource richness based on two-way analysis of variance (ANOVA). Bold font indicates significant differences (P < 0.05). TP, Total phosphorus; TC, Total carbon; TN, Total nitrogen; TS, Total sulfur.
| 土壤理化性质及微生物资源丰富度 Soil properties and microbial resources richness | 移除凋落物 Litter removal (df = 1) | 阻断根系 Root deprivation (df = 2) | 交互作用 Interaction (df = 2) | |||
|---|---|---|---|---|---|---|
| F | P | F | P | F | P | |
| 含水率 Moisture content (%) | 3.42 | 0.08 | 4.42 | < 0.05 | 0.68 | 0.52 |
| 酸碱度 pH | 0.22 | 0.65 | 0.58 | 0.57 | 2.37 | 0.12 |
| 总碳 TC (g/kg) | 6.29 | < 0.05 | 1.88 | 0.18 | 1.75 | 0.20 |
| 总氮 TN (g/kg) | 21.00 | < 0.001 | 2.51 | 0.11 | 1.85 | 0.18 |
| 总磷 TP (g/kg) | 5.76 | < 0.05 | 0.47 | 0.63 | 0.17 | 0.84 |
| 总硫 TS (g/kg) | 4.72 | < 0.05 | 0.0001 | 0.10 | 0.31 | 0.74 |
| 真菌丰富度 Fungal richness | 20.22 | < 0.001 | 2.74 | 0.09 | 0.55 | 0.59 |
| 细菌丰富度 Bacterial richness | 27.75 | < 0.001 | 3.55 | 0.05 | 3.76 | < 0.05 |
图3 移除凋落物和阻断根系对土壤理化性质和微生物资源丰富度的影响。不同字母表示不同根系处理间存在显著差异; 星号表示不同凋落物处理间存在显著差异。*** P < 0.001, ** P < 0.01, * P < 0.05。
Fig. 3 Effects of litter removal and root deprivation on soil physicochemical properties and microbial resource richness. Different letters indicate significant differences among root treatments; asterisks indicate significant differences between litter treatments. *** P < 0.001, ** P < 0.01, * P < 0.05. TP, Total phosphorus; TC, Total carbon; TN, Total nitrogen; TS, Total sulfur.
| 原生生物功能类群 Functional groups of protists | 移除凋落物 Litter removal (df = 1) | 阻断根系 Root deprivation (df = 2) | 交互作用 Interaction (df = 2) | |||
|---|---|---|---|---|---|---|
| F | P | F | P | F | P | |
| 食细菌者 Bacterivores | 44.30 | < 0.001 | 6.20 | < 0.01 | 0.38 | 0.70 |
| 食真核生物者 Eukaryvores | 30.59 | < 0.001 | 7.40 | < 0.01 | 4.12 | < 0.05 |
| 杂食者 Omnivores | 54.52 | < 0.001 | 4.76 | < 0.05 | 0.27 | 0.77 |
| 食碎屑者 Detritivores | 9.75 | < 0.01 | 2.73 | 0.09 | 4.16 | < 0.05 |
表2 基于双因素方差分析(ANOVA)的移除凋落物和阻断根系对不同原生生物功能类群丰富度的影响。加粗字体代表差异显著(P < 0.05)。
Table 2 Effects of litter removal and root deprivation on the richness of different protists functional groups based on two-way analysis of variance (ANOVA). Bold font indicates significant differences (P < 0.05).
| 原生生物功能类群 Functional groups of protists | 移除凋落物 Litter removal (df = 1) | 阻断根系 Root deprivation (df = 2) | 交互作用 Interaction (df = 2) | |||
|---|---|---|---|---|---|---|
| F | P | F | P | F | P | |
| 食细菌者 Bacterivores | 44.30 | < 0.001 | 6.20 | < 0.01 | 0.38 | 0.70 |
| 食真核生物者 Eukaryvores | 30.59 | < 0.001 | 7.40 | < 0.01 | 4.12 | < 0.05 |
| 杂食者 Omnivores | 54.52 | < 0.001 | 4.76 | < 0.05 | 0.27 | 0.77 |
| 食碎屑者 Detritivores | 9.75 | < 0.01 | 2.73 | 0.09 | 4.16 | < 0.05 |
图4 移除凋落物和阻断根系对食细菌者(A)、食真核生物者(B)、杂食者(C)和食碎屑者(D)丰富度的影响。不同字母表示不同根系处理间存在显著差异; 星号表示不同凋落物处理间存在显著差异。*** P < 0.001,** P < 0.01, * P < 0.05。
Fig. 4 Effects of litter removal and root deprivation on the richness of bacterivore (A), eukaryvore (B), omnivore (C), and detritivore (D) protists. Different letters indicate significant differences among root treatments. Asterisks denote significant differences between litter treatments. *** P < 0.001, ** P < 0.01, * P < 0.05.
图5 移除凋落物和阻断根系处理下食细菌者、食真核生物者、杂食者和食碎屑者群落组成的主坐标分析(PCoA)。颜色表示凋落物处理, 点形状和椭圆线型表示根系处理。椭圆表示95%的置信区间; R2表示移除凋落物和阻断根系对群落组成变异的解释度。
Fig. 5 Principal coordinate analysis (PCoA) of community composition of bacterivores, eukaryvores, omnivores, and detritivores protist under litter removal and root deprivation. Colors indicate litter treatments, while point shapes and ellipse line types represent root treatments. Ellipses denote 95% confidence intervals. R2 indicates the proportion of variation in community composition explained by litter removal and root deprivation.
图6 分段结构方程模型(PSEM)展示移除凋落物、阻断根系、土壤理化性质和微生物资源对土壤原生生物功能类群丰富度的直接和间接影响。红色箭头表示正相关性, 蓝色箭头表示负相关性; 实线表示显著(P < 0.05), 虚线表示不显著(P > 0.05)。*** P < 0.001, ** P < 0.01, * P < 0.05。线条旁的数值是标准化路径系数; 线条的粗细表示路径系数的显著程度; 作用越强线条越粗。R2表示模型中各变量对土壤理化性质、微生物资源以及原生生物功能类群丰富度变化的解释度。TC: 总碳; TN: 总氮; TS: 总硫; TP: 总磷。
Fig. 6 Piecewise structural equation models (PSEM) showing the direct and indirect effects of litter removal, root deprivation, and soil physicochemical properties and microbial resources on the richness of soil protist functional groups. Red arrows indicate positive correlations, and blue arrows indicate negative correlations. Solid lines represent significant effects (P < 0.05), whereas dashed lines represent non-significant effects (P > 0.05). *** P < 0.001, ** P < 0.01, * P < 0.05. Values adjacent to arrows indicate standardized path coefficients. Line thickness indicates the significance of path coefficients; thicker lines represent stronger effects. R² indicates the proportion of variance in soil physicochemical properties, microbial resources and protist functional group richness explained by the model variables. TC, Total carbon; TN, Total nitrogen; TS, Total sulfur; TP, Total phosphorus.
| 原生生物功能类群 Functional groups of protists | 效应 Effects | 移除凋落物 Litter removal | 阻断灌木根系 Shrub root deprivation | 阻断乔木根系 Tree root deprivation |
|---|---|---|---|---|
| 食细菌者 Bacterivores | 直接效应 Direct effects | 0 | 0 | -0.35 |
| 间接效应 Indirect effects | -0.61 | 0 | 0 | |
| 总效应 Total effects | -0.61 | 0 | -0.35 | |
| 食真核生物者 Eukaryvores | 直接效应 Direct effects | 0 | 0 | -0.33 |
| 间接效应 Indirect effects | -0.61 | 0 | 0.27 | |
| 总效应 Total effects | -0.61 | 0 | -0.06 | |
| 杂食者 Omnivores | 直接效应 Direct effects | 0 | -0.32 | -0.55 |
| 间接效应 Indirect effects | -0.77 | 0.13 | 0 | |
| 总效应 Total effects | -0.77 | -0.19 | -0.55 | |
| 食碎屑者 Detritivores | 直接效应 Direct effects | 0 | 0 | 0 |
| 间接效应 Indirect effects | -0.49 | 0.23 | 0 | |
| 总效应 Total effects | -0.49 | 0.23 | 0 |
表3 分段结构方程模型(PSEM)中移除凋落物及阻断根系对原生生物功能类群丰富度显著的直接、间接及总效应
Table 3 Significant direct, indirect, and total effects of litter removal and root deprivation on the richness of protist functional groups in the piecewise structural equation models (PSEM)
| 原生生物功能类群 Functional groups of protists | 效应 Effects | 移除凋落物 Litter removal | 阻断灌木根系 Shrub root deprivation | 阻断乔木根系 Tree root deprivation |
|---|---|---|---|---|
| 食细菌者 Bacterivores | 直接效应 Direct effects | 0 | 0 | -0.35 |
| 间接效应 Indirect effects | -0.61 | 0 | 0 | |
| 总效应 Total effects | -0.61 | 0 | -0.35 | |
| 食真核生物者 Eukaryvores | 直接效应 Direct effects | 0 | 0 | -0.33 |
| 间接效应 Indirect effects | -0.61 | 0 | 0.27 | |
| 总效应 Total effects | -0.61 | 0 | -0.06 | |
| 杂食者 Omnivores | 直接效应 Direct effects | 0 | -0.32 | -0.55 |
| 间接效应 Indirect effects | -0.77 | 0.13 | 0 | |
| 总效应 Total effects | -0.77 | -0.19 | -0.55 | |
| 食碎屑者 Detritivores | 直接效应 Direct effects | 0 | 0 | 0 |
| 间接效应 Indirect effects | -0.49 | 0.23 | 0 | |
| 总效应 Total effects | -0.49 | 0.23 | 0 |
| [1] | Adams RI, Miletto M, Taylor JW, Bruns TD (2013) Dispersal in microbes: Fungi in indoor air are dominated by outdoor air and show dispersal limitation at short distances. The ISME Journal, 7, 1262-1273. |
| [2] | Adl SM, Bass D, Lane CE, Lukeš J, Schoch CL, Smirnov A, Agatha S, Berney C, Brown MW, Burki F, Cárdenas P, Čepička I, Chistyakova L, Del Campo J, Dunthorn M, Edvardsen B, Eglit Y, Guillou L, Hampl V, Heiss AA, Hoppenrath M, James TY, Karnkowska A, Karpov S, Kim E, Kolisko M, Kudryavtsev A, Lahr DJG, Lara E, Le Gall L, Lynn DH, Mann DG, Massana R, Mitchell EAD, Morrow C, Park JS, Pawlowski JW, Powell MJ, Richter DJ, Rueckert S, Shadwick L, Shimano S, Spiegel FW, Torruella G, Youssef N, Zlatogursky V, Zhang Q (2019) Revisions to the classification, nomenclature, and diversity of eukaryotes. Journal of Eukaryotic Microbiology, 66, 4-119. |
| [3] | Beni A, Soki E, Lajtha K, Fekete I (2014) An optimized HPLC method for soil fungal biomass determination and its application to a detritus manipulation study. Journal of Microbiological Methods, 103, 124-130. |
| [4] | Bolyen E, Rideout JR, Dillon MR, Bokulich NA, Abnet CC, Al-Ghalith GA, Alexander H, Alm EJ, Arumugam M, Asnicar F, …, Warren J, Weber KC, Williamson CHD, Willis AD, Xu ZZ, Zaneveld JR, Zhang Y, Zhu Q, Knight R, Caporaso JG (2019) Reproducible, interactive, scalable and extensible microbiome data science using QIIME 2. Nature Biotechnology, 37, 852-857. |
| [5] | Bonkowski M, Clarholm M (2012) Stimulation of plant growth through interactions of bacteria and protozoa: Testing the auxiliary microbial loop hypothesis. Acta Protozoologica, 55, 237-247. |
| [6] | Bradford MA (2016) Re-visioning soil food webs. Soil Biology and Biochemistry, 102, 1-3. |
| [7] | Burki F, Roger AJ, Brown MW, Simpson AGB (2020) The new tree of eukaryotes. Trends in Ecology & Evolution, 35, 43-55. |
| [8] | Caporaso JG, Kuczynski J, Stombaugh J, Bittinger K, Bushman FD, Costello EK, Fierer N, Peña AG, Goodrich JK, Gordon JI, Huttley GA, Kelley ST, Knights D, Koenig JE, Ley RE, Lozupone CA, McDonald D, Muegge BD, Pirrung M, Reeder J, Sevinsky JR, Turnbaugh PJ, Walters WA, Widmann J, Yatsunenko T, Zaneveld J, Knight R (2010) QIIME allows analysis of high-throughput community sequencing data. Nature Methods, 7, 335-336. |
| [9] | Doblas-Miranda E, Sánchez-Piñero F, González-Megías A (2009) Different structuring factors but connected dynamics shape litter and belowground soil macrofaunal food webs. Soil Biology and Biochemistry, 41, 2543-2550. |
| [10] | Fang K, Kou YP, Tang N, Liu J, Zhang XY, He HL, Xia RX, Zhao WQ, Li DD, Liu Q (2024) Differential responses of soil bacteria, fungi and protists to root exudates and temperature. Microbiological Research, 286, 127829. |
| [11] | Fanin N, Bertrand I (2016) Aboveground litter quality is a better predictor than belowground microbial communities when estimating carbon mineralization along a land-use gradient. Soil Biology and Biochemistry, 94, 48-60. |
| [12] | Fekete I, Kotroczó Z, Varga C, Nagy PT, Várbíró G, Bowden RD, Tóth JA, Lajtha K (2014) Alterations in forest detritus inputs influence soil carbon concentration and soil respiration in a central-european deciduous forest. Soil Biology and Biochemistry, 74, 106-114. |
| [13] | Feng B, Chen L, Lou JY, Wang M, Xiong W, Sun RB, Ouyang Z, Sun ZG, Zhao BZ, Zhang JB (2025) Rhizosphere Cercozoa reflect the physiological response of wheat plants to salinity stress. Soil Ecology Letters, 7, 240268. |
| [14] | Frey SD, Elliott ET, Paustian K (1999) Bacterial and fungal abundance and biomass in conventional and no-tillage agroecosystems along two climatic gradients. Soil Biology and Biochemistry, 31, 573-585. |
| [15] | Fu XL, Guo DL, Wang HM, Dai XQ, Li ML, Chen FS (2017) Differentiating between root- and leaf-litter controls on the structure and stability of soil micro-food webs. Soil Biology and Biochemistry, 113, 192-200. |
| [16] | Fu XL, Wang JL, Di YB, Wang HM (2015) Differences in fine-root biomass of trees and understory vegetation among stand types in subtropical forests. PLoS ONE, 10, e0128894. |
| [17] | Geddes N, Dunkerley D (1999) The influence of organic litter on the erosive effects of raindrops and of gravity drops released from desert shrubs. Catena, 36, 303-313. |
| [18] | Geisen S, Mitchell EAD, Wilkinson DM, Adl S, Bonkowski M, Brown MW, Fiore-Donno AM, Heger TJ, Jassey VEJ, Krashevska V, Lahr DJG, Marcisz K, Mulot M, Payne R, Singer D, Anderson OR, Charman DJ, Ekelund F, Griffiths BS, Rønn R, Smirnov A, Bass D, Belbahri L, Berney C, Blandenier Q, Chatzinotas A, Clarholm M, Dunthorn M, Feest A, Fernández LD, Foissner W, Fournier B, Gentekaki E, Hájek M, Helder J, Jousset A, Koller R, Kumar S, La Terza A, Lamentowicz M, Mazei Y, Santos SS, Seppey CVW, Spiegel FW, Walochnik J, Winding A, Lara E (2017) Soil protistology rebooted: 30 fundamental questions to start with. Soil Biology and Biochemistry, 111, 94-103. |
| [19] | Hao YZ, Zhao JY, Lu M, Wang Q, Peng WQ, Chen Z (2020) Effect of plant roots on river bank stabilization after composite vegetation planting. Journal of Hydroecology, 41(3), 42-50. (in Chinese with English abstract) |
| [郝由之, 赵进勇, 路明, 王琦, 彭文启, 陈卓 (2020) 复合植被根系作用对生态岸坡稳定性的影响. 水生态学杂志, 41(3), 42-50.] | |
| [20] | Huang WJ, Spohn M (2015) Effects of long-term litter manipulation on soil carbon, nitrogen, and phosphorus in a temperate deciduous forest. Soil Biology and Biochemistry, 83, 12-18. |
| [21] | Juhos K, Madarász B, Kotroczó Z, Béni Á, Makádi M, Fekete I (2021) Carbon sequestration of forest soils is reflected by changes in physicochemical soil indicators—A comprehensive discussion of a long-term experiment on a detritus manipulation. Geoderma, 385, 114918. |
| [22] | Kelly JJ, Favila E, Hundal LS, Marlin JC (2007) Assessment of soil microbial communities in surface applied mixtures of illinois river sediments and biosolids. Applied Soil Ecology, 36, 176-183. |
| [23] | Li MJ, Niu BL, Chen ZC, Liu YC, Liu SR (2025) Effects of tree species diversity on soil organic carbon in natural forests of Quercus aliena var. acuteserrata in Baotianman. Acta Ecologica Sinica, 45, 10687-10697. (in Chinese with English abstract) |
| [李铭杰, 牛保亮, 陈志成, 刘彦春, 刘世荣 (2025) 树种多样性对宝天曼天然栎林土壤有机碳的影响. 生态学报, 45, 10687-10697.] | |
| [24] | Li Z, Bluhm SL, Scheu S, Pollierer MM (2022) Amino acid isotopes in functional assemblages of Collembola reveal the influence of vertical resource heterogeneity and root energy supply on trophic interactions in soil food webs. Soil Biology and Biochemistry, 174, 108815. |
| [25] | Nguyen BT, Chen QL, Yan ZZ, Li CY, He JZ, Hu HW (2021) Distinct factors drive the diversity and composition of protistan consumers and phototrophs in natural soil ecosystems. Soil Biology and Biochemistry, 160, 108317. |
| [26] | Niu XD, Chen ZC, Yan CY, Niu BL, Liu SR (2025) A dataset of half-hour meteorological observations at Henan Baotianman Forest Ecosystem National Observation and Research Station (2015-2023). China Scientific Data, 10(1), 294-304. (in Chinese with English abstract) |
| [牛晓栋, 陈志成, 闫崇宇, 牛保亮, 刘世荣 (2025) 2015-2023年河南宝天曼森林生态系统国家野外科学观测研究站半小时尺度气象数据集. 中国科学数据(中英文网络版), 10(1), 294-304.] | |
| [27] | Noh NJ, Chung H, Ryu SR, Son Y, Lee SK, Yoon TK, Yang AR, Kim J (2012) Changes in soil properties of Abies holophylla and Quercus-dominated stands 4 years after trenching. Scandinavian Journal of Forest Research, 27, 597-604. |
| [28] | Ogée J, Brunet Y (2002) A forest floor model for heat and moisture including a litter layer. Journal of Hydrology, 255, 212-233. |
| [29] | Oliverio AM, Geisen S, Delgado-Baquerizo M, Maestre FT, Turner BL, Fierer N (2020) The global-scale distributions of soil protists and their contributions to belowground systems. Science Advances, 6, eaax8787. |
| [30] | R Core Team (2025) R: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing. https://www.R-project.org/. (accessed on 2026-03-23) |
| [31] | Sanderman J, Baldock JA, Amundson R (2008) Dissolved organic carbon chemistry and dynamics in contrasting forest and grassland soils. Biogeochemistry, 89, 181-198. |
| [32] | Sang CP, Wan XH, Yu ZP, Wang MH, Lin Y, Huang ZQ (2017) Effects of litter and root exclusion on soil microbial community composition and function of four plantations in subtropical sandy coastal plain area, China. Chinese Journal of Applied Ecology, 28, 1184-1196. (in Chinese with English abstract) |
| [桑昌鹏, 万晓华, 余再鹏, 王民煌, 林宇, 黄志群 (2017) 凋落物和根系去除对滨海沙地土壤微生物群落组成和功能的影响. 应用生态学报, 28, 1184-1196.] | |
| [33] | Scott-Denton LE, Rosenstiel TN, Monson RK (2006) Differential controls by climate and substrate over the heterotrophic and rhizospheric components of soil respiration. Global Change Biology, 12, 205-216. |
| [34] | Shao YH, Wang XL, Zhao J, Wu JP, Zhang WX, Neher DA, Li YX, Lou YP, Fu SL (2016) Subordinate plants sustain the complexity and stability of soil micro-food webs in natural bamboo forest ecosystems. Journal of Applied Ecology, 53, 130-139. |
| [35] | Stefan G, Cornelia B, Jörg R, Michael B (2014) Soil water availability strongly alters the community composition of soil protists. Pedobiologia, 57, 205-213. |
| [36] | Stoeck T, Bass D, Nebel M, Christen R, Jones MDM, Breiner HW, Richards TA (2010) Multiple marker parallel tag environmental DNA sequencing reveals a highly complex eukaryotic community in marine anoxic water. Molecular Ecology, 19, 21-31. |
| [37] | Xiao Y, Chen HX, Qiu LJ, Zhang Y, Wan SZ (2021) Effects of understory removal on soil microbial community composition in subtropical Phyllostachys edulis plantations. Chinese Journal of Applied Ecology, 32, 3089-3096. (in Chinese with English abstract) |
| [肖意, 陈慧娴, 邱丽君, 张扬, 万松泽 (2021) 林下植物剔除对毛竹林土壤微生物群落结构的影响. 应用生态学报, 32, 3089-3096.] | |
| [38] | Zhalnina K, Louie KB, Hao Z, Mansoori N, Da Rocha UN, Shi S, Cho H, Karaoz U, Loqué D, Bowen BP, Firestone MK, Northen TR, Brodie EL (2018) Dynamic root exudate chemistry and microbial substrate preferences drive patterns in rhizosphere microbial community assembly. Nature Microbiology, 3, 470-480. |
| [39] | Zhao CC, Guo EH, Shao YH, Zhang WX, Zhang CL, Liu YC, Li Y, Zou XM, Fu SL (2021) Impacts of litter addition and root presence on soil nematode community structure in a young Eucalyptus plantation in Southern China. Forest Ecology and Management, 479, 118633. |
| [40] | Zhou Z, Lu JZ, Preiser J, Widyastuti R, Scheu S, Potapov A (2023) Plant roots fuel tropical soil animal communities. Ecology Letters, 26, 742-753. |
| [41] | Zhu HQ, Gong L, Luo Y, Tang JH, Ding ZL, Li XC (2022) Effects of litter and root manipulations on soil bacterial and fungal community structure and function in a Schrenk’s spruce (Picea schrenkiana) forest. Frontiers in Plant Science, 13, 849483. |
| [42] | Zieger SL, Eissfeller V, Maraun M, Scheu S (2015) Incorporation of carbon and nitrogen from leaf litter differing in structural compounds into soil microarthropods of a deciduous forest. Pedobiologia, 58, 219-227. |
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