1. 青海大学 农牧学院,青海,西宁,810016
2. 青海大学 省部共建三江源生态与高原农牧业国家重点实验室,青海,西宁,810016
3. 中国科学院 西北高原生物研究所, 青海省寒区恢复生态学重点实验室,青海,西宁,810008
4. 青海省民和县农牧局, 青海 民和,810800
纸质出版:2019
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孙华方, 李希来, 金立群, 等. 黄河源区人工草地植被群落和土壤养分变化[J]. 水土保持通报, 2019,39(3):25-30.
Sun Huafang, Li Xilai, Jin Liqun, et al. Variation of Vegetation Community and Soil Nutrients of Artificial Grassland in Source Area of Yellow River[J]. Bulletin of Soiland Water Conservation, 2019, 39(3): 25-30.
孙华方, 李希来, 金立群, 等. 黄河源区人工草地植被群落和土壤养分变化[J]. 水土保持通报, 2019,39(3):25-30. DOI: 10.13961/j.cnki.stbctb.2019.03.005.
Sun Huafang, Li Xilai, Jin Liqun, et al. Variation of Vegetation Community and Soil Nutrients of Artificial Grassland in Source Area of Yellow River[J]. Bulletin of Soiland Water Conservation, 2019, 39(3): 25-30. DOI: 10.13961/j.cnki.stbctb.2019.03.005.
[目的]研究黄河源区不同年限人工草地植被群落特征和土壤养分的动态变化,揭示高寒地区人工草地稳定机制与演替规律,为退化高寒草甸(湿地)的近自然恢复和缩短退化草地恢复时间提供理论依据。[方法]选择黄河源区青海省玛沁县3,11,17 a单播垂穗披碱草人工草地,对植被与土壤养分特征进行调查。[结果]随着种植年限增加,人工草地优势种垂穗披碱草盖度降低,植物总盖度、生物结皮盖度、杂类草盖度以及生殖枝数量呈倒“V”型变化,而原生植被莎草科植物盖度、物种多样性逐渐增加,17 a人工草地中莎草科植物的盖度是3,11 a的10倍;人工草地土壤养分中全氮、全钾、速效氮、速效钾以及有机质随年限增加呈现积累趋势,土壤pH值逐渐趋于中性。土壤全氮含量在不同恢复年限之间差异最大,平均准确率降低度为25.71,有机质含量次之,其平均准确率降低度为18.55,而全钾含量及均匀度指数最小,平均准确率降低度均小于5。[结论]高寒地区人工草地群落结构和土壤营养随着建植时间的延长在逐渐恢复,建植17 a的人工草地土壤全氮、有机质含量仅是原生高寒草甸土壤的50%左右,因此,17 a人工草地土壤养分完全恢复还需要较长时间。
[Objective] The variation of vegetation community and soil nutrients in artificial grassland was studied and the long-term successional mechanism of artificial grasslands was explored in order to provide theoretical basis for the near-natural restoration of degraded alpine meadow (wetland).[Methods] The vegetation communities and soil nutrients of artificial grassland with different planting years (3
11 and 17 years) were investigated in Maqin County of Qinghai Province
the source region of the Yellow River. Random forest analysis was used to determine the variation of vegetation community and soil nutrient characteristics of artificial grassland under different restoration years.[Results] The coverage of dominant species Elymus nutans decreased with the increase of restoration years
while the total coverage
biological crust coverage
weed coverage and reproductive branch number showed an inverted "V" shape of variation. The Cyperaceae coverage and species richness increased gradually with the increase of restoration years. The coverage of Cyperaceae in 17 years artificial grassland was 10 times of that in 3 and 11 years. The total nitrogen
total potassium
available nitrogen
available potassium and organic matter in soil increased with the increase of restoration years. The soil pH value tended to be neutral with the increase of restoration years. The greatest differences among vegetation with different restoration years was the soil total nitrogen content
with the average accuracy degraded about 25.71. Followed by the organic matter content
the average accuracy degraded about 18.55. The differences of total potassium content and Pielou index among vegetation with different restoration years were the smallest
and the average index degraded was less than 5.[Conclusion] The vegetation community structure and soil nutrient of artificial grassland with 17 years restoration are gradually recovering
but the soil total nitrogen and organic matter content of the artificial grassland is only half of the original alpine meadow soil
and it will take a long time for the soil nutrient to recover completely.
王莺,李耀辉,孙旭映.黄河源区域生态环境演变与对策建议[J].干旱气象,2013,31(3):550-557.
Li Xilai, Perry G L W, Brierley G, et al. Quantitative assessment of degradation classifications for degraded alpine meadows(Heitutan), Sanjiangyuan, Western China[J]. Land Degradation & Development, 2015,25(5):417-427.
Li Xilai, Perry G, Brierley G J. Grassland Ecosystems of the Yellow River Source Zone:Degradation and Restoration[M]//Brierley G J, Li Xilai. Landscape and Ecosystem Diversity, Dynamics and Management in the Yellow River Source Zone. Springer International Publishing,2016:137-165.
Li Xilai, Gao J, Zhang Jing. A topographic perspective on the distribution of degraded meadows and their changes on the Qinghai-Tibet Plateau, West China[J]. Land Degradation & Development,2018,29(6):1574-1582.
马玉寿,施建军,董全民,等.人工调控措施对"黑土型"退化草地垂穗披碱草人工植被的影响[J].青海畜牧兽医杂志,2006,36(2):1-3.
刘斌,罗全华,常文哲,等.不同林草植被覆盖度的水土保持效益及适宜植被覆盖度[J].中国水土保持科学, 2008,6(6):68-73.
伍星,李辉霞,傅伯杰,等.三江源地区高寒草地不同退化程度土壤特征研究[J].中国草地学报,2013,35(3):77-84.
张蕊,王媛,马丽娜等.三江源区退化人工草地、"黑土滩"和天然草地植物群落物种多样性[J].草地学报,2014,22(6):1171-1178.
孙磊,刘玉,武高林,等.藏北退化草地群落生物量与土壤养分的关系[J].草业科学,2016,33(6):1062-1069.
杨崇曜,李恩贵,陈慧颖,等.内蒙古西部自然植被的物种多样性及其影响因素[J].生物多样性,2017,25(12):1303-1312.
周华坤,赵新全,赵亮,等.高山草甸垂穗披碱草人工草地群落特征及稳定性研究[J].中国草地学报,2007,29(2):13-25.
赵丽娅,李元哲,陈红兵,等.科尔沁沙地恢复过程中地上定植群落与土壤种子库特征及其关系研究[J].生态环境学报,2018,27(2):199-208.
陈玫妃,曾辉,王钧,等.青藏高原高寒草地土壤水分生态特征研究现状[J].中国草地学报,2015,37(2):94-101.
白晓,张兰慧,王一博,等.祁连山区不同土地覆被类型下土壤水分变异特征[J].水土保持研究,2017,24(2):17-25.
朱美壮,王根绪,肖瑶,等.青藏高原多年冻土区高寒草甸土壤水分入渗变化研究[J].冰川冻土,2017,39(6):1316-1325.
秦莉,沈玉君,李国学,等.不同C/N比堆肥碳素物质变化规律研究[J].农业环境科学学报,2010,29(7):1388-1393.
Chamizo S, Cantón Y, Miralles I, et al. Biological soil crust development affects physicochemical characteristics of soil surface in semiarid ecosystems[J]. Soil Biology & Biochemistry.2012,49:96-105.
常晶晶,徐丽,薛晶月,等.放牧强度对若尔盖高寒草甸土壤有机质和微生物的影响[J].草业学报,2018,27(1):22-31.
杨希智,王长庭,字洪标,等.三江源区不同建植年限人工草地土壤微生物群落结构特征[J].应用与环境生物学报,2015,21(2):341-349.
字洪标,刘敏,阿的鲁骥,等.三江源区不同建植年限对人工草地土壤微生物功能多样性的影响[J].生态学杂志, 2017,36(4):978-987.
冯瑞章,周万海,龙瑞军,等.江河源区不同退化程度高寒草地土壤物理、化学及生物学特征研究[J].土壤通报, 2010,41(2):263-269.
王长庭,曹广民,王启兰,等.三江源地区不同建植期人工草地植被特征及其与土壤特征的关系[J].应用生态学报,2007,18(11):2426-2431.
张玉萍,宋乃平,王兴,等.不同放牧制度对荒漠草原植物多样性及土壤理化性状的影响[J].北方园艺,2018(19):109-115.
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