Advancing the use of minirhizotrons in wetlands

被引:56
作者
Iversen, C. M. [1 ]
Murphy, M. T. [2 ]
Allen, M. F. [3 ]
Childs, J. [1 ]
Eissenstat, D. M. [4 ]
Lilleskov, E. A. [5 ]
Sarjala, T. M. [6 ]
Sloan, V. L. [7 ]
Sullivan, P. F. [8 ,9 ]
机构
[1] Oak Ridge Natl Lab, Div Environm Sci, Oak Ridge, TN 37831 USA
[2] McGill Univ, Dept Geog, Montreal, PQ, Canada
[3] Univ Calif Riverside, Ctr Conservat Biol, Riverside, CA 92521 USA
[4] Penn State Univ, Dept Hort, University Pk, PA 16802 USA
[5] USDA Forest Serv, No Res Stn, Houghton, MI USA
[6] Finnish Forest Res Inst, Parkano, Finland
[7] Univ Sheffield, Dept Anim & Plant Sci, Sheffield S10 2TN, S Yorkshire, England
[8] Univ Alaska Anchorage, Environm & Nat Resources Inst, Anchorage, AK USA
[9] Univ Alaska Anchorage, Dept Biol Sci, Anchorage, AK USA
基金
美国能源部; 美国国家科学基金会;
关键词
Fine roots; Minirhizotron; Wetlands; Peatlands; Methodology; NET PRIMARY PRODUCTION; FINE-ROOT DYNAMICS; BLACK SPRUCE FORESTS; WATER-TABLE; NUTRIENT AVAILABILITY; MYCORRHIZAL STATUS; NITROGEN DYNAMICS; NORTHERN PEATLAND; PLANT BIOMASS; BRANCH ORDER;
D O I
10.1007/s11104-011-0953-1
中图分类号
S3 [农学(农艺学)];
学科分类号
0901 ;
摘要
Background Wetlands store a substantial amount of carbon (C) in deep soil organic matter deposits, and play an important role in global fluxes of carbon dioxide and methane. Fine roots (i.e., ephemeral roots that are active in water and nutrient uptake) are recognized as important components of biogeochemical cycles in nutrient-limited wetland ecosystems. However, quantification of fine-root dynamics in wetlands has generally been limited to destructive approaches, possibly because of methodological difficulties associated with the unique environmental, soil, and plant community characteristics of these systems. Non-destructive minirhizotron technology has rarely been used in wetland ecosystems. Scope Our goal was to develop a consensus on, and a methodological framework for, the appropriate installation and use of minirhizotron technology in wetland ecosystems. Here, we discuss a number of potential solutions for the challenges associated with the deployment of minirhizotron technology in wetlands, including minirhizotron installation and anchorage, capture and analysis of minirhizotron images, and upscaling of minirhizotron data for analysis of biogeochemical pools and parameterization of land surface models. Conclusions The appropriate use of minirhizotron technology to examine relatively understudied fine-root dynamics in wetlands will advance our knowledge of ecosystem C and nutrient cycling in these globally important ecosystems.
引用
收藏
页码:23 / 39
页数:17
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