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請用此 Handle URI 來引用此文件: http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/71035
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dc.contributor.advisor梁偉立
dc.contributor.authorChun Chiuen
dc.contributor.author邱均zh_TW
dc.date.accessioned2021-06-17T04:49:33Z-
dc.date.available2023-08-01
dc.date.copyright2018-08-01
dc.date.issued2018
dc.date.submitted2018-07-31
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dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/71035-
dc.description.abstractFine roots play critical roles in carbon and nutrient cycles in forest ecosystems. Thus, understanding fine root dynamics for characterizing carbon and nutrient cycles in forest ecosystems is important. The optical scanner method is useful for monitoring fine root dynamics. Few studies have applied this method in mountainous forests with various species and sloping conditions in Taiwan. In this study, we investigated the sampling position for scanned image acquisition and calculated the recovery time of fine root systems following soil disturbance caused by scanner box installation. This study was conducted 1) to clarify fine root distribution around single trees on slopes in a broad-leaved forest and in an adjacent Japanese cedar (Cryptomeria japonica) plantation and 2) to determine the differences in the fine root dynamics of the natural broad-leaved forest and the adjacent Japanese cedar plantation forest by using the optical scanner method. Moreover, 3) based on the derived data, the recovery time of fine root systems following soil disturbance was determined.
To achieve the first objective, this study used the soil coring method for quantifying the distribution of fine root density (FRD) around tree trunks in the natural forest (number of target trees [n] = 10) and in the Japanese cedar plantation forest (n = 5). Both forest areas are part of the Experimental Forest of National Taiwan University located on Mount Fong-Huang in Xitou tract. Soil samples were collected from three positions around each sampled tree trunk along a slope (i.e., 1.0 m away in the upper, horizontal, and lower directions from the tree trunk). To achieve the second and third objectives, this study applied the optical scanner method beside the sample trees. Data were collected for two dominant tree species (n = 4 for each species) in the natural forest and Japanese cedar trees (n = 4) in the Japanese cedar plantation from May 2017 to April 2018. Using the temporal changes in fine root biomass (FRB) as indicated in the data from the first year after soil disturbance, this study estimated the recovery time of fine root systems in the forests.
First, large variations were identified in the FRD around the tree trunks on the slopes. These variations were not correlated with the sampling positions in either the natural forest or the Japanese cedar plantation forest, suggesting that slope position was not a critical concern and that the sampling number was of more important for FRD estimates. The only difference in FRD between the two forests was the mean value for FRD, which was approximately twice as large for the natural forest (651.1 g m−2) as that for the Japanese cedar forest (309.6 g m−2). Second, fine root production was more active than decomposition in the study period. Fine root production was highly correlated with FRB, whereas fine root decomposition was not. This finding suggested that FRB dynamics were mainly determined by the fluctuation in fine root production during the study period. This study identified two temporal patterns for FRB in the two forests: linear increase (Pattern I) was observed in the FRB of the Japanese cedar trees and three broad-leaved trees, and a saturation-shaped-curve pattern (Pattern Ⅱ) was observed in the FRB of five broad-leaved trees. The patterns were associated with distinct temporal changes in fine root production. Trees with Pattern I exhibited active fine root production in the later part of the study period (autumn–winter), whereas trees characterized by Pattern II were inactive in fine root production at that time. Third, for the five broad-leaved trees that exhibited Pattern II, FRB reached a stable state 5–6 months after the soil disturbance caused by equipment installation. However, FRB did not reach a stable state in the Japanese cedar trees or the three broad-leaved trees characterized by Pattern I. These results suggested that the recovery time of fine root systems may vary among individual trees. One year may have been insufficient for some trees at the study sites to recover FRB after soil disturbance from installation of equipment for the optical scanner method.
en
dc.description.provenanceMade available in DSpace on 2021-06-17T04:49:33Z (GMT). No. of bitstreams: 1
ntu-107-R05625047-1.pdf: 4267526 bytes, checksum: 7c74e5883959b1cd401eeec2ae2e378c (MD5)
Previous issue date: 2018
en
dc.description.tableofcontents口試委員會審定書 1
摘要 2
Abstract 4
Contents 6
Figures 8
Tables 10
Chapter 1 Introduction 11
1.1 Background 11
1.2 Objectives of this study 17
Chapter 2 Materials and methods 17
2.1 Site description 18
2.1.1 Location and environment 18
2.1.2 Stand properties 20
2.2 Soil coring 22
2.2.1 Field measurements and equipment 22
2.2.2 Analysis 26
2.3 Optical scanner methods 28
2.3.1 Field measurements 28
2.3.2 Processing and analysis of fine root images 32
2.3.3 Verification of analysis ability 35
Chapter 3 Result and discussion for fine root distributions 37
3.1 Ambient fine root distribution of tree individuals in sloping condition 37
3.1.1 Representativeness of sample species 37
3.1.2 Distribution of fine root density at the natural forest site 39
3.1.3 Distribution of fine root density at the Japanese cedar plantation site 42
3.2 The difference of FRD between the natural forest and the Japanese cedar plantation 45
Chapter 4 Result and discussion for fine root dynamics 49
4.1 Temporal variation of fine root biomass, production and decomposition of the natural forest after box installation 49
4.2 Temporal variation of fine root biomass, production and decomposition of the Japanese cedar plantation site after box installation 57
4.3 The temporal patterns of fine root biomass, production and decomposition in natural and artificial (plantation) forest 63
Chapter 5 Conclusion 68
References 71
Appendix 75
dc.language.isoen
dc.title臺灣中部溪頭鳳凰山天然林及柳杉人工林之細根分布與動態zh_TW
dc.titleDistributions and Dynamics of Fine Roots in a Natural Forest and a Japanese Cedar (Cryptomeria japonica) Plantation in Mount Fong-Huang in Xitou, Central Taiwanen
dc.typeThesis
dc.date.schoolyear106-2
dc.description.degree碩士
dc.contributor.coadvisor久米朋宣(Tomonori Kume)
dc.contributor.oralexamcommittee陳秋萍
dc.subject.keyword細根,動態,天然林,柳杉,季節變異,空間變異,zh_TW
dc.subject.keywordfine root,dynamic,Japanese cedar,natural forest,spatial variation,seasonal variation,en
dc.relation.page77
dc.identifier.doi10.6342/NTU201802243
dc.rights.note有償授權
dc.date.accepted2018-07-31
dc.contributor.author-college生物資源暨農學院zh_TW
dc.contributor.author-dept森林環境暨資源學研究所zh_TW
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