1. 中国科学院水利部水土保持研究所黄土高原土壤侵蚀与旱地农业国家重点实验室, 陕西 杨凌,712100
2. 中国科学院大学,北京,100049
3. 西北农林科技大学林学院, 陕西 杨凌,712100
4. 西北农林科技大学水土保持研究所, 陕西 杨凌,712100
[ "张凯(1993-),女,在读硕士研究生,主要从事植物生态学研究。E-mail:zk930321@163.com" ]
纸质出版:2018
移动端阅览
张凯, 徐慧敏, 李秧秧. 坡向与植物群落对水蚀风蚀交错带土壤有机碳氮的影响[J]. 水土保持学报, 2018,32(6):156-165.
ZHANG Kai, XU Huimin, LI Yangyang. Effects of Slope Aspects and Plant Community Types on Soil Organic Carbon and Nitrogen in the Crisscross Area of Wind-Water Erosion[J]. 2018, 32(6): 156-165.
张凯, 徐慧敏, 李秧秧. 坡向与植物群落对水蚀风蚀交错带土壤有机碳氮的影响[J]. 水土保持学报, 2018,32(6):156-165. DOI: 10.13870/j.cnki.stbcxb.2018.06.024.
ZHANG Kai, XU Huimin, LI Yangyang. Effects of Slope Aspects and Plant Community Types on Soil Organic Carbon and Nitrogen in the Crisscross Area of Wind-Water Erosion[J]. 2018, 32(6): 156-165. DOI: 10.13870/j.cnki.stbcxb.2018.06.024.
以黄土高原北部水蚀风蚀交错带六道沟流域内的1个支沟为对象,通过植被调查和采样分析,研究了坡向和植物群落类型对土壤有机碳(SOC)、全氮(TN)含量、碳氮比(C/N)和有机碳氮密度(SOCD、TND)的影响。结果表明:(1)坡向对0—20 cm土壤SOC和TN含量及0—60 cm C/N均有显著影响。SOC、TN含量及C/N分别表现为:半阴坡 > 半阳坡 > 沟头半阴坡 > 半阳坡=沟头及半阳坡 > 半阴坡≥沟头的趋势;(2)植物群落对0—10 cm SOC和TN含量及0—20 cm C/N均有显著影响。半阴坡分布的3种豆科群落达乌里胡枝子、紫花苜蓿及白花草木樨间土壤碳氮差异不显著,但均显著高于禾本科的长芒草群落;半阳坡分布的达乌里胡枝子和紫花苜蓿群落SOC和TN含量相当,均显著高于茵陈蒿群落(菊科)和长芒草群落;沟头的达乌里胡枝子群落SOC、TN显著高于长芒草。豆科草本植物更有利于促进土壤碳氮的积累;(3)坡向主要影响表层0—20 cm SOCD和TND,其对60 cm剖面SOCD和TND贡献率分别为45%~55%和47%~53%。不同植物群落下土壤表层及整个剖面SOCD和TND均有显著差异。研究支沟内SOCD平均为2.13 kg/m2,远低于黄土高原其他地区。上述结果对于水蚀风蚀交错带土壤碳氮储量的精确评估及植被合理建造有一定指导价值。
A branch gully of Liudaogou watershed in the wind-water erosion crisscross region of the northern Loess Plateau was selected as the object
and the effects of slope aspects and plant community types on soil organic carbon (SOC)
total nitrogen (TN) content
ratio of carbon-nitrogen (C/N) and soil organic carbon and nitrogen density (SOCD
TND) were studied through vegetation survey and sampling analysis. The results showed that:(1) Slope aspects had significant effects on the SOC and TN contents in 0-20 cm
and C/N in 0-60 cm. The SOC
TN contents and C/N followed the order of semi-shady slope > semi-sunny slope > gully-head
semi-shady slope > semi-sunny slope=gully-head
and semi-sunny slope > semi-shady slope ≥ gully-head
respectively. (2) Plant communities had significant effects on the SOC and TN contents in 0-10 cm and C/N in 0-20 cm. There was no significant difference in SOC and TN contents between three kinds of leguminous communities growing in the semi-shady slope
namely
Lespedeza davurica
alfalfa and sweet clover
but they were significantly higher than that of the Stipa bungeana community. The SOC and TN contents in Lespedeza davurica and alfalfa communities were similar in the semi-sunny slope
which were significantly higher than those of the Artemisia capillaris and Stipa bungeana communities. The SOC and TN contents in Lespedeza davurica community were significantly higher than that of the Stipa bungeana community in the gully-head
indicating that legume herb was more conducive to the accumulation of soil carbon and nitrogen in the study area. (3) Slope aspects mainly affected the SOCD and TND in surface layer of 0-20 cm
and their contribution to SOCD and TND of 60 cm soil profile were 45%~55% and 47%~53%
respectively. There were significant differences in SOCD and TND between the surface layer and the whole soil profile under different plant community types. The average SOCD in the studied branch gully was estimated to be 2.13 kg/m2
which was far lower than other parts of the Loess Plateau. These results had important role in evaluating soil carbon and nitrogen storage accurately and rational construction of vegetation in the crisscross area of wind-water erosion on the Loess Plateau.
Fu X, Shao M, Wei X, et al. Soil organic carbon and total nitrogen as affected by vegetation types in Northern Loess Plateau of China[J].Geoderma,2010,155(1):31-35.
Stockmann U, Adams M A, Crawford J W, et al. The knowns, known unknowns and unknowns of sequestration of soil organic carbon[J].Agriculture Ecosystems and Environment,2013,164(4):80-99.
Lal R. Potential of desertification control to sequester carbon and mitigate the greenhouse effect[J].Climatic Change,2001,51(1):35-72.
Chen L F, He Z B, Zhu X, et al. Impacts of afforestation on plant diversity, soil properties, and soil organic carbon storage in a semi-arid grassland of northwestern China[J].Catena,2016,147:300-307.
Xin Z, Qin Y, Yu X. Spatial variability in soil organic carbon and its influencing factors in a hilly watershed of the Loess Plateau, China[J].Catena,2016,137:660-669.
Jobbagy E G, Jackson R B. The vertical distribution of soil organic carbon and its relation to climate and vegetation[J].Ecological Applications,2000,10(2):423-436.
Vesterdal L, Schmidt I K, Callesen I, et al. Carbon and nitrogen in forest floor and mineral soil under six common European tree species[J].Forest Ecology and Management,2008,255(1):35-48.
Choudhury B U, Mohapatra K P, Das A, et al. Spatial variability in distribution of organic carbon stocks in the soils of North East India[J].Current Science,2013,104(5):604-614.
Eckert S, Engesser M. Assessing vegetation cover and biomass in restored erosion areas in Iceland using SPOT satellite data[J].Applied Geography,2013,40(2):179-190.
Wang Y, Fu B, Lü Y, et al. Effects of vegetation restoration on soil organic carbon sequestration at multiple scales in semi-arid Loess Plateau, China[J].Catena,2011,85(1):58-66.
Schwanghart W, Jarmer T. Linking spatial patterns of soil organic carbon to topography:A case study from south-eastern Spain[J].Geomorphology,2011,126(1):252-263.
Sun W, Zhu H, Guo S. Soil organic carbon as a function of land use and topography on the Loess Plateau of China[J].Ecological Engineering,2015,83:249-257.
Lai Z, Zhang Y, Liu J, et al. Fine-root distribution, production, decomposition, and effect on soil organic carbon of three revegetation shrub species in northwest China[J].Forest Ecology and Management,2016,359(14):381-388.
孙文义,郭胜利.黄土丘陵沟壑区小流域土壤有机碳空间分布及其影响因素[J].生态学报,2011,31(6):1604-1616.
Huang Y M, Liu D, An S S. Effects of slope aspect on soil nitrogen and microbial properties in the Chinese Loess region[J].Catena,2015,125:135-145.
Zhang C, Liu G B, Xue S. Soil organic carbon and total nitrogen storage as affected by land use in a small watershed of the Loess Plateau, China[J]. European Journal of Soil Biology,2013,54(1):16-24.
Zhao J, Dong Y, Wang Y, et al. Natural vegetation restoration is more beneficial to soil surface organic and inorganic carbon sequestration than tree plantation on the Loess Plateau of China[J].Science of the Total Environment,2014,485(1):615-623.
刘伟,程积民,陈芙蓉,等.黄土高原中部草地土壤有机碳密度特征及碳储量[J].草地学报,2011,19(3):425-431.
唐克丽.黄土高原水蚀风蚀交错区治理的重要性与紧迫性[J].中国水土保持,2000(11):11-12.
徐少君,曾波,苏晓磊,等.基于RS/GIS的重庆缙云山自然保护区植被及碳储量密度空间分布研究[J].生态学报,2012,32(7):2174-2184.
董鸣.陆地生物群落调查观测与分析[M].北京:中国标准出版社,1997:1-23.
鲍士旦.土壤农化分析[M].3版.北京:中国农业出版社,1999:25-49.
孟国欣,查同刚,张晓霞,等.植被类型和地形对黄土区退耕地土壤有机碳垂直分布的影响[J].生态学杂志,2017,36(9):2447-2454.
朱猛,刘蔚,秦燕燕,等.祁连山森林草原带坡面尺度土壤有机碳分布[J].中国沙漠,2016,36(3):741-748.
刘旻霞,王刚.高寒草甸植物群落多样性及土壤因子对坡向的响应[J].生态学杂志,2013,32(2):259-265.
Rorison I H, Sutton F, Hunt R. Local climate, topography and plant growth in Lathkill Dale NNR. I. A twelve-year summary of solar radiation and temperature[J].Plant Cell and Environment,1986,9(1):49-56.
Nichols J D. Relation of organic carbon to soil properties and climate in the Southern Great Plains[J].Soil Science Society of America Journal,1984,48(6):1382-1384.
陶贞,次旦朗杰,张胜华,等.草原土壤有机碳含量的控制因素[J].生态学报,2013,33(9):2684-2694.
Liu L, Duan Z H, Xu M K, et al. Effect of monospecific and mixed Cunninghamialanceolata plantations on microbial community and two functional genes involved in nitrogen cycling[J].Plant and Soil,2010,327(1/2):413-428.
Florinsky I V, Mcmahon S, Burton D L. Topographic control of soil microbial activity:A case study of denitrifiers[J].Geoderma,2004,119(1):33-53.
Berendsen R L, Pieterse C M, Bakker P A. The rhizospheremicrobiome and plant health[J].Trends in Plant Science,2012,17(8):478-486.
Wu G, Liu Y, Tian F, et al. Legumes functional group promotes soil organic carbon and nitrogen storage by increasing plant diversity[J].Land Degradation and Development,2017,28(4):1336-1344.
刘学彤,魏艳春,杨宪龙,等.水蚀风蚀交错带不同退耕模式对土壤有机碳及全氮的影响[J].应用生态学报,2016,27(1):91-98.
Zhao J, Wang X, Wang X, et al. Legume-soil interactions:Legume addition enhances the complexity of the soil food web[J].Plant and Soil,2014,385(1/2):273-286.
王邵军,曹子林,李小英,等.滇池湖滨带不同植被类型土壤碳、氮时空分布特征[J].南京林业大学学报(自然科学版),2013,37(5):55-59.
何亚龙.黄土高原退耕地土壤水分养分与碳密度的研究[D].陕西杨凌:西北农林科技大学,2011.
温仲明,焦峰,刘宝元,等.黄土高原森林草原区退耕地植被自然恢复与土壤养分变化[J].应用生态学报,2005,16(11):2025-2029.
李裕元,邵明安,郑纪勇,等.黄土高原北部草地的恢复与重建对土壤有机碳的影响[J].生态学报,2007,27(6):2279-2287.
方精云,杨元合,马文红,等.中国草地生态系统碳库及其变化[J].中国科学(生命科学),2010,40(7):566-576.
邓蕾.黄土高原生态系统碳固持对植被恢复的响应机制[D].陕西杨凌:西北农林科技大学,2014.
0
浏览量
1490
下载量
4
CSCD
关联资源
相关文章
相关作者
相关机构
京公网安备11010802024621