Effects of composition and habitat differences on litter decomposition and nutrient release characteristics of Abies georgei var. smithii in southeastern Tibet
DAI Songjia1, ZHOU Chenni2,3,4, DUAN Fei2,3,4, FANG Jiangping2,3,4, LONG Chunlin1
1. College of Life and Environmental Sciences, Minzu University of China, 100081, Beijing, China; 2. Research Institute of Tibet Plateau Ecology, Tibet Agriculture & Animal Husbandry University, 860000, Nyingchi, Tibet, China; 3. Key Laboratory of Forest Ecology in Tibet Plateau(Tibet Agriculture & Animal Husbandry University), Ministry of Education, 860000, Nyingchi, Tibet, China; 4. United Key Laboratories of Ecological Security, Tibet Autonomous Region, 860000, Nyingchi, Tibet, China
Abstract:[Background] Litter decomposition is one of the important links of material cycle and energy flow in forest ecosystem. There are few reports on the litter decomposition and nutrient release of typical natural dark coniferous forests in Tibet. The purpose of this study is to provide basic data and theoretical basis for in-depth understanding of the material cycle process of forest ecosystem in high altitude and cold environment. [Methods] Three types of samples (leaf sample, natural sample, and branch sample) from 3 sample plots (in forest, outside forest and beside forest) were selected in Sejila Mountain, Tibet. The litter of Abies georgei var. smithii forest was collected in December 2016. At the beginning of each month in 2017, 3 bags of litters were collected from each sample plot, and the litter retention rate and monthly decomposition rate were calculated. The content of C, N, P, and K was determined by concentrated sulfuric acid-potassium dichromate method, Kjeldahl method, molybdenum blue colorimetric spectrophotometry, flame spectrophotometry. [Results] 1) The monthly decomposition rate of litter was leaf sample (2.21%) > natural sample (2.17%) > branch sample (1.70%), and IF (2.17%) > OF (1.94%) > BF (1.93%). 2) The decomposition time of 95% of natural sample, leaf sample and branch sample litter in the same habitat with different components was 8.96 years, 10.02 years and 13.18 years. 3) The decomposition time of 95% of IF, OF, and BF with the same component was 8.96 years, 10.01 years and 10.84 years. 4) The release rates of C and N were significantly positively correlated with the components, while the release rates of P and K were negatively correlated with the components. 5) The release rates of C, N, P and K were significantly or very significantly and positively correlated with the habitat. 6) There were significant differences in C/N, C/P and N/P among different habitats. 7) There was a very significant negative correlation between C/N and habitat, no significant correlation between C/P and habitat, and an extremely significant positive correlation between N/P and habitat. [Conclusions] Different litter components and habitat conditions have significant effects on litter decomposition rate and nutrient release characteristics, and the effects of components and habitats vary.
代松家, 周晨霓, 段斐, 方江平, 龙春林. 组分和生境差异对藏东南原始冷杉林凋落物分解和养分释放特征的影响[J]. 中国水土保持科学, 2020, 18(6): 72-80.
DAI Songjia, ZHOU Chenni, DUAN Fei, FANG Jiangping, LONG Chunlin. Effects of composition and habitat differences on litter decomposition and nutrient release characteristics of Abies georgei var. smithii in southeastern Tibet. SSWC, 2020, 18(6): 72-80.
LI L, ZENG D, YU Z, et al. Impact of litter quality and soil nutrient availability on leaf decomposition rate in a semi-arid grassland of Northeast China[J]. Journal of Arid Environments, 2011, 75(9):787.
[2]
SALAH Y M S, SCHOLES M C. Effect of temperature and litter quality on decomposition rate of Pinus patula needle litter[J]. Procedia Environmental Sciences, 2011, 6(1):180.
[3]
SARI K, JUHA P, HANNA R, et al. Gene expression responses of paper birch (Betula papyrifera) to elevated CO2 and O3 during leaf maturation and senescence[J]. Environmental Pollution, 2010, 158(4):959.
[4]
SANTONJA M, FERNANDEZ C, PROFFIT M, et al. Plant litter mixture partly mitigates the negative effects of extended drought on soil biota and litter decomposition in a Mediterranean oak forest[J]. Journal of Ecology, 2017, 105(3):801.
[5]
MONROY S, MENENDEZ M, BASAGUREN A, et al. Drought and detritivores determine leaf litter decomposition in calcareous streams of Ebro catchment (Spain)[J]. Science of the Total Environment, 2016, 573(12):1450.
[6]
KASURINEN A, SILFVER T, ROUSI M, et al. Warming and ozone exposure effects on silver birch (Betula pendula Roth) leaf litter quality, microbial growth and decomposition[J]. Plant and Soil, 2017, 414(1/2):127.
[7]
吴庆贵, 吴福忠, 潭波, 等. 高山森林林窗对凋落叶分解的影响[J]. 生态学报, 2016, 36(12):3537. WU Qinggui,WU Fuzhong,TAN Bo, et al. Effects of gap sizes on foliar litter decomposition in alpine forests[J]. Acta Ecologica Sinica, 2016, 36(12):3537.
[8]
吴庆贵, 谭波, 杨万勤, 等. 亚高山森林林窗大小对凋落叶木质素降解的影响[J]. 生态学报, 2016, 36(18):5701. WU Qinggui, TAN Bo, YANG Wanqin, et al. Effects of gap sizes on the lignin degradation of foliar litter in a subalpine forest[J]. Acta Ecologica Sinica, 2016, 36(18):5701.
[9]
刘洋, 张健, 冯茂松. 巨桉人工林凋落物数量、养分归还量及分解动态[J]. 林业科学, 2006, 42(7):1. LIU Yang, ZHANG Jian, FENG Maosong. Dynamics of litter production, nutrient return and decomposition of four Eucalyptus grandis plantation[J]. Scientia Silvae Sinicae, 42(7):1.
[10]
金龙, 吴志祥, 杨川, 等. 不同林龄橡胶凋落物叶分解特性与有机碳动态研究[J]. 热带作物学报, 2015, 36(4):698. JIN Long, WU Zhixiang, YANG Chuan, et al. Leaf-litter decomposition characteristics and carbon dynamics affected by forest ages in rubber plantations[J]. Chinese Journal of Tropical Crops, 2015, 36(4):698.
[11]
丁新景, 解国磊, 敬如岩, 等. 黄河三角洲不同人工刺槐混交林凋落物分解特性[J]. 水土保持学报, 2016, 30(4):249. DING Xinjing, XIE Guolei, JING Ruyan, et al. Decomposition characteristic of litters in different mixed forest of Robinia pseudoacacia in Yellow River Delta[J]. Journal of Soil and Water Conservation, 2016, 30(4):249.
[12]
吴鹏, 王襄平, 张新平, 等. 东北地区森林凋落叶分解速率与气候、林型、林分光照的关系[J]. 生态学报, 2016, 36(8):2223. WU Peng, WANG Xiangping, ZHANG Xinping, et al. Effects of climate, forest type and light availability on litter decomposition rate in forests of Northeast China[J]. Acta Ecologica Sinica, 2016, 36(8):2223.
[13]
刘涛, 孙守琴, 邱阳. 川西亚高山生态系统三种典型植物凋落物分解动态特征[J]. 山地学报, 2017, 35(5):663. LIU Tao, SUN Shouqin, QIU Yang. Dynamics and differences in the decomposition of litters from three dominating plants in subalpine ecosystems in western Sichuan China[J]. Mountain Research, 2017, 35(5):663.
[14]
PATRA A K, ABBADIE L, CLAYS-JOSSERAND A, et al. Effects of management regime and plant species on the enzyme activity and genetic structure of N-fixing, denitrifying and nitrifying bacterial communities in grassland soils[J]. Environmental Microbiology, 2006, 8(6):1005.
[15]
陈金玲, 金光泽, 赵凤霞. 小兴安岭典型阔叶红松林不同演替阶段凋落物分解及养分变化[J]. 应用生态学报, 2010, 21(9):2209. CHEN Jinling, JIN Guangze, CHEN Fengxia. Litter decomposition and nutrient dynamics at different succession stages of typical mixed broadleaved-Korean pine forest in Xiaoxing'an Mountains, China[J]. Chinese Journal of Applied Ecology, 2010, 21(9):2209.
[16]
任立宁, 刘世荣, 王一, 等. 毛竹和林下植被芒萁凋落物分解特征研究[J]. 林业科学研究, 2018, 31(5):91. REN Lining, LIU Shirong, WANG Yi, ea al. Decomposition characteristics of litter of Phyllostachys edulis and Dicranopteris pedate [J]. Forest Research, 2018, 31(5):91.
[17]
BERGLUND S L, AGREN G I, EKBLAD A. Carbon and nitrogen transfer in leaf litter mixtures[J]. Soil Biology and Biochemistry, 2013, 57(9):341.
[18]
李忠文, 闫文德, 郑威, 等. 亚热带樟树-马尾松混交林凋落物量及养分动态特征[J]. 2013, 33(24):7707. LI Zhongwen, YAN Wende, ZHENG Wei, et al. Litter fall production and nutrient dynamic of Cinnamomum camphora and Pinus massoniana mixed forests in subtropics China[J]. Acta Ecologica Sinica, 2013, 33(24):7707.
[19]
鲁志云, 宋亮, 王训, 等. 哀牢山森林凋落物与腐殖质及土壤的生态化学计量特征[J]. 山地学报, 2017, 35(3):274. LU Zhiyun, SONG Liang, WANG Xun, et al. Ecological stoichiometry characteristic of the litterfall-humus-soil continnum systems under different successional stages of the subtropical forest in SW China[J]. Mountain Research, 2017, 35(3):274.