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科学研究

长期排水造林对云贵高原亚热带泥炭藓沼泽土壤理化性质的影响

  • 杨浚恒 ,
  • 崔海军 ,
  • 石珣珣 ,
  • 郭应 ,
  • 张璞韬 ,
  • 毕晓婷
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  • 1.西南林业大学 云南省高原湿地保护修复与生态服务重点实验室,昆明 650224
    2.西南林业大学 国家高原湿地研究中心/湿地学院,昆明 650224
    3.盘州市自然资源局,贵州 盘州 553537
杨浚恒(1992-),女,云南曲靖人,硕士研究生,主要研究方向为高原泥炭沼泽湿地保护与恢复。Email:348742561@qq.com

收稿日期: 2022-12-16

  修回日期: 2023-02-10

  网络出版日期: 2023-05-05

基金资助

云南省教育厅项目(2019Y0142);国家自然科学基金(32160272)

Effects of Long-Term Drainage for Afforestation on Soil Physicochemical Properties of Subtropical Sphagnum Mire in Yunnan-Guizhou Plateau

  • Junheng YANG ,
  • haijun CUI ,
  • Xunxun SHI ,
  • Ying GUO ,
  • Putao ZHANG ,
  • Xiaoting BI
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  • 1. Yunnan Key Laboratory of Plateau Wetland Conservation,Restoration and Ecological Services,Southwest Forestry University,Kunming 650224,China
    2. National Plateau Wetlands Research Center/College of Wetlands,Southwest Forestry University,Kunming 650224,China
    3. Natural Resources Bureau of Panzhou city,Panzhou,Guizhou 553537,China

Received date: 2022-12-16

  Revised date: 2023-02-10

  Online published: 2023-05-05

摘要

探究排水造林对亚热带泥炭藓沼泽土壤理化性质的影响,为科学保护与恢复该类型湿地提供理论基础。选择贵州娘娘山湿地天然泥炭藓沼泽为对照样地,选择经立地条件相似的泥炭藓沼泽排水造林20年形成的柳杉林为处理样地,比较二者表层(0~10cm)土壤理化性质的差异。主要结果:1)泥炭藓沼泽土壤总碳含量、总氮含量、pH、碳与磷质量比(C:P)、氮与磷质量比(N:P)、速效钾含量、硝态氮含量、铵态氮含量、土壤质量含水量显著高于柳杉林土壤相应的指标值(P<0.05);泥炭藓沼泽土壤容重显著低于柳杉林土壤容重;2)主成分分析显示,长期营造柳杉林后土壤理化性质总体已发生明显分异;3)土壤总碳含量与总氮含量呈极显著正相关(P<0.01),且二者与C:P,N:P,速效钾含量、硝态氮含量、质量含水量呈极显著正相关(P<0.01),与土壤容重呈极显著负相关(P<0.01),C:P,N:P,铵态氮含量、硝态氮含量、速效钾含量两两之间呈极显著正相关(P<0.01)或显著正相关(P<0.05);土壤质量含水量与容重呈极显著负相关(P<0.01)。总之,泥炭藓沼泽长期营造柳杉林后,表层土壤大量有机质发生氧化分解,土壤含水量显著降低,容重显著增加,土壤磷限制缓解,土壤理化性质总体发生明显分异,由泥炭土转变为矿质土。

本文引用格式

杨浚恒 , 崔海军 , 石珣珣 , 郭应 , 张璞韬 , 毕晓婷 . 长期排水造林对云贵高原亚热带泥炭藓沼泽土壤理化性质的影响[J]. 林草资源研究, 2023 , 0(1) : 80 -86 . DOI: 10.13466/j.cnki.lyzygl.2023.01.010

Abstract

The effects of drainage and afforestation on the physical and chemical properties of soil in subtropical Sphagnum mire were explored to provide a theoretical basis for scientific protection and restoration of this type of wetland.Natural Sphagnum mire in Niangniang Mountain wetland,Guizhou was selected as the control site,and Cryptomeria fortunei forest formed by drainage for afforestation in the sphagnum mire with similar site conditions for 20 years was selected as the treatment site,and the differences in the physical and chemical properties of the surface (0~10cm) soil between the two kinds of sites were compared.Main results:1) The total soil carbon content,total nitrogen content,pH,mass ratio of carbon to phosphorus (C:P),mass ratio of nitrogen to phosphorus (N:P),available potassium content,nitrate nitrogen content,ammonium nitrogen content and soil mass water content of the Sphagnum mire were significantly higher than the corresponding index values of the Cryptomeria fortunei forest (P<0.05).The soil bulk density of Sphagnum mire was significantly lower than that of the Cryptomeria fortunei forest.2) PCA showed that the overall physical and chemical properties of the soil had changed significantly after the long-term afforestation of Cryphieria fortunea forest.3) Total soil carbon content was significantly positively correlated with total nitrogen content(P<0.01),and both of them were significantly positively correlated with C:P,N:P,available potassium content,nitrate nitrogen content,mass water content,respectively (P<0.01),and significantly negatively correlated with bulk density(P<0.01).C:P,N:P,ammonium nitrogen content,nitrate nitrogen content and available potassium content were very significantly or significantly positively correlated with each other.Mass water content was negatively correlated with bulk density(P<0.01).In conclusion,after a long-term afforestation of Cryptomeria fortuneana forest in Sphagnum mire,a large amount of organic matter in the surface soil oxidized and decomposed,soil water content decreased significantly,bulk density increased significantly,soil phosphorus limitation was relieved,and the soil physical and chemical properties were significantly different overall,and the peat soil was transformed into mineral soil.

参考文献

[1] 黄咸雨, 张志麒, 王红梅, 等. 神农架大九湖泥炭湿地关键带监测进展[J]. 地球科学, 2017, 42(6):1026-1038.
[2] Li Tingting, Lei Yun, Dai Can, et al. Effects of both substrate and nitrogen and phosphorus fertilizer on Sphagnum palustre growth in subtropical high-mountain regions and implications for peatland recovery[J]. Wetlands Ecology and Management, 2018, 26(4):651-663.
[3] 卜兆君, 杨允菲, 代丹, 等. 长白山泥炭沼泽桧叶金发藓种群的年龄结构与生长分析[J]. 应用生态学报, 2005, 16(1):44-48.
[4] Kandel T P, Laerke P E, Elsgaard L. Annual emissions of CO2,CH4 and N2O from a temperate peat bog:Comparison of an undrained and four drained sites under permanent grass and arable crop rotations with cereals and potato[J]. Agricultural and Forest Meteorology, 2018, 256:470-481.
[5] Sloan T J, Payne R J, Anderson A R, et al. Peatland afforestation in the UK and consequences for carbon storage[J]. Mires and Peat, 2019, 23:1-17.
[6] 何春梅, 张朝晖, 王智慧, 等. 贵州麻若平台泥炭藓沼泽中泥炭藓持水特性及其与土壤营养元素关系研究[J]. 植物科学学报, 2020, 38(5):618-626.
[7] Kraigher B, Stres B, Hacin J, et al. Microbial activity and community structure in two drained fen soils in the Ljubljana Marsh[J]. Soil Biology & Biochemistry, 2006, 38(9):2762-2771.
[8] Ausec L, Kraigher B, Mandic-Mulec I. Differences in the activity and bacterial community structure of drained grassland and forest peat soils[J]. Soil Biology & Biochemistry, 2009, 41(9):1874-1881.
[9] Nieminen M, Sarkkola S, Lauren A. Impacts of forest harvesting on nutrient,sediment and dissolved organic carbon exports from drained peatlands:A literature review,synthesis and suggestions for the future[J]. Forest Ecology and Management, 2017, 392:13-20.
[10] Li Tingting, Wang Zhengxiang, Bu Guijun, et al. Effects of microtopography and water table on Sphagnum palustre L.in subtropical high mountains and implications for peatland restoration[J]. Journal of Bryology, 2019, 41(2):121-134.
[11] Urbanová Z, Bárta J. Effects of long-term drainage on microbial community composition vary between peatland types[J]. Soil Biology & Biochemistry, 2016, 92:16-26.
[12] 斯南雍茜, 葛继稳, 李愈, 等. 神农架大九湖亚高山典型泥炭湿地土壤养分特征分析[J]. 水土保持学报, 2020, 34(5):321-326.
[13] Straková P, Niemi R M, Freeman C, et al. Litter type affects the activity of aerobic decomposers in a boreal peatland more than site nutrient and water level regimes[J]. Biogeosciences, 2011, 8(9):2741-2755.
[14] 孟祥久. 排水造林对泥炭沼泽湿地碳循环的影响概述[J]. 湿地科学与管理, 2013, 9(4):60-64.
[15] 邵宗仁, 赵光影, 臧淑英, 等. 排水造林对小兴安岭沼泽湿地土壤酶活性及氮含量的影响[J]. 环境工程, 2016, 34(11):122-126.
[16] Minkkinen K, Vasander H, Jauhiainen S, et al. Post-drainage changes in vegetation composition and carbon balance in Lakkasuo mire,Central Finland[J]. Plant and Soil, 1999, 207(1):107-120.
[17] Andersen R, Chapman S J, Artz R R E. Microbial communities in natural and disturbed peatlands:A review[J]. Soil Biology & Biochemistry, 2013, 57:979-994.
[18] 张云萍, 刘石宁, 徐志伟, 等. 长白山白江河天然和排水泥炭沼泽土壤酶活性研究[J]. 湿地科学, 2019, 17(4):445-452.
[19] Cleveland C C, Liptzin D. C:N:P stoichiometry in soil:Is there a “Redfield ratio” for the microbial biomass?[J]Biogeochemistry, 2007, 85(3):235-252.
[20] Hill B H, Elonen C M, Jicha T M, et al. Ecoenzymatic stoichiometry and microbial processing of organic matter in northern bogs and fens reveals a common P-limitation between peatland types[J]. Biogeochemistry, 2014, 120(1-3):203-224.
[21] Ka?tovská E, Straková P, Edwards K Z, et al. Cotton-grass and blueberry have opposite effect on peat characteristics and nutrient transformation in peatland[J]. Ecosystems, 2018, 21(3):443-458.
[22] Larmola T, Leppanen S M, Tuittila E S, et al. Methanotrophy induces nitrogen fixation during peatland development[J]. Proceedings of the National Academy of Sciences of the United States of America, 2013, 111(2):734-739.
[23] Verhoeven J T A, Liefveld W M. The ecological significance of organochemical compounds in Sphagnum[J]. Acta Botanica Neerlandica, 1997, 46(2):117-130.
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